JPH07198593A - Chromaticity measuring method and apparatus in sewage or drain disposal - Google Patents
Chromaticity measuring method and apparatus in sewage or drain disposalInfo
- Publication number
- JPH07198593A JPH07198593A JP33563093A JP33563093A JPH07198593A JP H07198593 A JPH07198593 A JP H07198593A JP 33563093 A JP33563093 A JP 33563093A JP 33563093 A JP33563093 A JP 33563093A JP H07198593 A JPH07198593 A JP H07198593A
- Authority
- JP
- Japan
- Prior art keywords
- chromaticity
- wavelength
- absorbance
- sample water
- water
- 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
Links
- 238000000034 method Methods 0.000 title claims abstract description 50
- 239000010865 sewage Substances 0.000 title claims abstract description 25
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 87
- 238000002835 absorbance Methods 0.000 claims abstract description 28
- 238000005259 measurement Methods 0.000 claims abstract description 22
- 238000011088 calibration curve Methods 0.000 claims abstract description 7
- 239000012086 standard solution Substances 0.000 claims description 13
- 238000004364 calculation method Methods 0.000 claims description 10
- 238000004065 wastewater treatment Methods 0.000 claims description 4
- 238000012937 correction Methods 0.000 claims description 3
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 abstract description 16
- 238000012544 monitoring process Methods 0.000 abstract description 9
- 229910017052 cobalt Inorganic materials 0.000 abstract description 8
- 239000010941 cobalt Substances 0.000 abstract description 8
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 abstract description 8
- 229910052697 platinum Inorganic materials 0.000 abstract description 8
- 239000007788 liquid Substances 0.000 abstract description 2
- 239000000523 sample Substances 0.000 description 26
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 10
- CLBRCZAHAHECKY-UHFFFAOYSA-N [Co].[Pt] Chemical compound [Co].[Pt] CLBRCZAHAHECKY-UHFFFAOYSA-N 0.000 description 10
- 238000000691 measurement method Methods 0.000 description 10
- 235000019646 color tone Nutrition 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 239000002351 wastewater Substances 0.000 description 7
- 238000000862 absorption spectrum Methods 0.000 description 5
- 230000001276 controlling effect Effects 0.000 description 5
- 238000010998 test method Methods 0.000 description 5
- 238000004737 colorimetric analysis Methods 0.000 description 4
- 239000008213 purified water Substances 0.000 description 3
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 2
- 239000002656 Distearyl thiodipropionate Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 229910052801 chlorine Inorganic materials 0.000 description 2
- 239000003086 colorant Substances 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000004043 dyeing Methods 0.000 description 2
- 230000031700 light absorption Effects 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000008399 tap water Substances 0.000 description 2
- 235000020679 tap water Nutrition 0.000 description 2
- 238000002834 transmittance Methods 0.000 description 2
- 230000000007 visual effect Effects 0.000 description 2
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 description 1
- 241000894006 Bacteria Species 0.000 description 1
- 241000195493 Cryptophyta Species 0.000 description 1
- 241000588724 Escherichia coli Species 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 238000011481 absorbance measurement Methods 0.000 description 1
- 230000032900 absorption of visible light Effects 0.000 description 1
- 230000002353 algacidal effect Effects 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- GVPFVAHMJGGAJG-UHFFFAOYSA-L cobalt dichloride Chemical compound [Cl-].[Cl-].[Co+2] GVPFVAHMJGGAJG-UHFFFAOYSA-L 0.000 description 1
- 230000000295 complement effect Effects 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 239000004021 humic acid Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000012488 sample solution Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 230000001953 sensory effect Effects 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 230000000638 stimulation Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000011550 stock solution Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000011179 visual inspection Methods 0.000 description 1
Landscapes
- Investigating Or Analysing Materials By Optical Means (AREA)
- Sewage (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は下水処理又は排水処理工
程における色度測定方法及び装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a chromaticity measuring method and apparatus in a sewage treatment or wastewater treatment process.
【0002】[0002]
【従来の技術】一般に河川などから取水した原水とか下
水2次処理水を浄化するには、凝集沈殿池で原水中に凝
集剤を注入,混合し、撹拌及び滞留処理により原水中の
懸濁物質(砂,粘土,藻類等の有機物等)を凝集して沈
澱,分離する。このプロセスでは殺藻処理や鉄,マンガ
ンなどの色度成分の除去を目的とした塩素処理が組み込
まれている。2. Description of the Related Art Generally, in order to purify raw water taken from rivers or secondary treated water of sewage, a coagulant is injected and mixed in raw water in a coagulating sedimentation tank, and suspended substances in the raw water are treated by stirring and retaining. (Sand, clay, algae, and other organic matter) are aggregated, precipitated, and separated. This process incorporates chlorine treatment for the purpose of algicidal treatment and removal of chromaticity components such as iron and manganese.
【0003】一方、近年下水道の普及率が高くなるのに
つれて、都市域における水資源として下水処理水の有効
活用が期待されている。特に年間80億m3を越すとい
われる下水処理水は、都市域における安定した水資源と
しての可能性を有しており、さまざまな形態での処理水
再利用の期待がかけられているが、その一つとして修景
用水とか親水用水等への再利用がある。[0003] On the other hand, with the increasing prevalence of sewerage in recent years, effective utilization of sewage treated water is expected as a water resource in urban areas. In particular, treated sewage water, which is said to exceed 8 billion m 3 annually, has the potential as a stable water resource in urban areas, and there are expectations for reuse of treated water in various forms. One of them is reuse for landscape water or hydrophilic water.
【0004】修景用水としての再利用形態は、既存水路
への処理水導入とか堀等の滞水としての利用、公園等の
アメニティ施設の池とか噴水、せせらぎ等の用水として
の使用が考えられる。又、親水用水とは水遊び等の人間
が触れることを前提とした再利用水である。As a form of reuse as scenic water, it is considered that the treated water is introduced into an existing water channel or used as water retention such as a moat, or as water for amenity facilities such as parks, fountains, murmuring, etc. . Further, hydrophilic water is reused water that is presumed to be touched by humans such as playing in water.
【0005】このように下水処理水を修景用水・親水用
水として再利用するには、再利用水の衛生学的安全性と
か感覚的快適性及び再利用技術、補完的な方策について
十分な検討を行う必要がある。As described above, in order to reuse the treated sewage water as scenic water / hydrophilic water, sufficient consideration is given to hygienic safety of the reused water, sensory comfort, reuse technology, and complementary measures. Need to do.
【0006】下水処理水を再利用するため留意すべき基
本的水質項目には、これまでの下水処理水に求められて
いた処理水質に加えて、大腸菌群数とか臭気及び色度等
の除去の外、BODとかpH,濁度が問題となる。特に
上記大腸菌とか臭気及び色度の除去には高度処理,例え
ばオゾン処理により有機物,無機物の分解を行う方法が
考えられ、且つ実際のプラントにも採用されている。即
ち、オゾンは強い酸化力と殺菌力を持ち、他の方法に比
べて効果的に殺菌、脱臭及び脱色を行うことができる。
特に浄水の分野では、塩素処理に起因するTHM(トリ
ハロメタン)対策と原水の水質悪化対策を目的として近
時オゾン処理が実用化されている。In order to reuse the treated sewage water, basic water quality items to be noted include, in addition to the treated water quality required for the treated sewage water up to now, removal of the number of coliform bacteria, odor and chromaticity. Outside, BOD, pH, and turbidity are problems. In particular, in order to remove Escherichia coli, odor and chromaticity, a method of decomposing organic substances and inorganic substances by advanced treatment, for example, ozone treatment, can be considered and is also adopted in an actual plant. That is, ozone has a strong oxidizing power and sterilizing power, and can effectively sterilize, deodorize and decolorize as compared with other methods.
Particularly in the field of water purification, ozone treatment has recently been put into practical use for the purpose of measures against THM (trihalomethane) caused by chlorine treatment and measures against deterioration of water quality of raw water.
【0007】このような背景から、上述した物質の除去
を目的とする高度処理システムの監視及び制御を実施す
るに際して、色度は重要な指標の一つであり、この色度
を自動的且つ連続的に測定する方法の実現が望まれてい
る。From such a background, chromaticity is one of the important indexes when monitoring and controlling an advanced processing system for the purpose of removing the above-mentioned substances, and this chromaticity is automatically and continuously measured. It is desired to realize a method for measuring in real time.
【0008】色度は本来上水処理において使用されてい
る指標であり、上水試験方法(1985年版)には「色
度とは水中に含まれる溶解性物質及びコロイド性物質が
呈する類黄色ないし黄褐色の程度をいい、主として地質
に由来するフミン質による呈色と同じ色調の色について
測られるものである。」と定義されている。通常精製水
1リットルに色度標準液中の白金1mg及びコバルト
0.5mgを含む時の呈色に相当するものを1度として
いる。[0008] Chromaticity is an index originally used in the treatment of clean water. According to the clean water test method (1985 version), "chromaticity is a kind of yellow or yellow which is exhibited by soluble substances and colloidal substances contained in water. It is the degree of yellow-brown color, and is mainly measured for colors with the same color tone as that of the humic substances derived from the geology. " Usually, one degree corresponds to the coloration when 1 liter of purified water contains 1 mg of platinum and 0.5 mg of cobalt in the chromaticity standard solution.
【0009】上水試験方法による色度測定方法は、一般
に白金・コバルト法を採用するのが通例である。この方
法は色度標準原液として、塩化白金酸カリウム(K2P
tCl6)2.49g及び塩化コバルト(CoCl2・6
H2O)2.02gをメスフラスコ1リットルに採り、
塩酸200mlで溶かした後、精製水を加えて全量を1
リットルとし、この色度標準原液100mlをメスフラ
スコ1リットルに採り、精製水を加えて全量を1リット
ルとして色度標準液として、試料液を比色法により測定
する方法である(上水試験方法4.色度の項を参照)。In general, the platinum / cobalt method is adopted as the method for measuring chromaticity by the water test method. This method uses potassium chloroplatinate (K 2 P
Tcl 6) 2.49 g and cobalt chloride (CoCl 2 · 6
H 2 O) 2.02 g was taken in a 1-liter volumetric flask,
After dissolving with 200 ml of hydrochloric acid, add purified water to bring the total volume to 1
This is a method of measuring 100 ml of this chromaticity standard stock solution in 1 liter of a volumetric flask, adding purified water to bring the total volume to 1 liter and using the chromaticity standard solution as a chromaticity standard solution, and measuring the sample solution by the colorimetric method. 4. See chromaticity section).
【0010】即ち、色度の主原因となるフミン酸の光吸
収の極大は紫外部にあり、可視光の吸収は極めて小さい
が、色度自体は人の感覚に訴える色の程度をいうもので
あるから肉眼により測らなければならない。That is, the maximum light absorption of humic acid, which is the main cause of chromaticity, is in the ultraviolet region and the absorption of visible light is extremely small, but the chromaticity itself is the degree of color appealing to human senses. Because it's there, you have to measure it with the naked eye.
【0011】更に上水試験方法「5.色の単色表示」及
び工場排水試験方法(JIS K0102)「11.色
度」によれば、「色の単色表示とは主波長(色相),刺
激純度及び明度によって表したものをいい、色度の測定
ができない着色水の色の状態を示すもの」と規定されて
いる。主波長とは試料の呈色に最も寄与している光の波
長をいい、色相とは主波長によって呈せられる色の鮮や
かさをいい、明度とは明るさをいう。Further, according to the water supply test method “5. Single color display of color” and the factory drainage test method (JIS K0102) “11. Chromaticity”, “single color display of color means dominant wavelength (hue), stimulation purity”. And the lightness, which indicates the state of the color of colored water for which the chromaticity cannot be measured. " The dominant wavelength refers to the wavelength of light that contributes most to the coloration of the sample, the hue refers to the vividness of the color exhibited by the dominant wavelength, and the lightness refers to the brightness.
【0012】単色表示の測定は、光電分光光度計を用い
て可視光線(400〜700nm)の各波長における検
水の透過率を測定して3刺激値を求め、これから刺激純
度を算定し、併せて明度及び主波長(色相)を求める方
法である。3刺激値とは、眼が色から受ける刺激が主と
して赤色に強く感じるもの、緑色に強く感じるもの及び
青紫色に強く感じるものとがあり、これら3種類の刺激
の混合の割合によって感覚的に識別されるものであるた
め、眼に対してそれぞれの刺激を与える光の波長群を
X,Y,Zの系列にまとめ、各波長の光における検水の
透過率を系列毎に集計して得た値に係数を乗じて求め
る。The monochromatic display is measured by measuring the transmittance of the sample water at each wavelength of visible light (400 to 700 nm) using a photoelectric spectrophotometer to obtain three stimulus values. It is a method for obtaining the brightness and the dominant wavelength (hue). The three stimulus values include those in which the stimulus that the eye receives from the color mainly feel strongly in red, those in which it strongly feels in green, and those in which it strongly feels in blue-purple. Therefore, the wavelength groups of light that give each stimulus to the eye are grouped into X, Y, and Z series, and the transmittance of the sample water for each wavelength of light is tabulated and obtained. Calculate by multiplying the value by a coefficient.
【0013】更に修景用水・親水用水の色度測定法とし
て、平成2年に建設省から出された「下水処理水の修景
・親水利用水質検討マニュアル(案)」では、前記上水
試験方法の「4.色度」の測定方法にしたがうとされて
いる。但し染色排水等が流入する下水処理水については
検討を要する旨の記述がある。Furthermore, as a method for measuring the chromaticity of landscape water / hydrophilic water, in the “Scenic Treatment Water Landscape / Hydrophilic Water Quality Examination Manual (draft)” issued by the Ministry of Construction in 1990, the above-mentioned water supply test was conducted. It is said to follow the measuring method of "4. chromaticity" in the method. However, there is a statement that sewage treatment water, such as dyeing wastewater, needs to be examined.
【0014】又、水道協会雑誌,第62巻第2号(平成
5年2月号)には、厚生省による「水道水質に関する基
準の制定について」と題する記事があり、これによれば
波長390nm付近で吸光度を測定し、色度標準液で作
成した検量線から試料水の色度を算定する方法(以下、
透過光測定法と略称する)が記載されている。In addition, there is an article titled "Establishment of Standards for Water Quality in Tap Water" by the Ministry of Health and Welfare in the Water Supply Association Magazine, Vol. 62, No. 2 (February, 1993 issue), which says that the wavelength is around 390 nm. Method to calculate the chromaticity of the sample water from the calibration curve created with the chromaticity standard solution by measuring the absorbance with
(Abbreviated as transmitted light measurement method).
【0015】[0015]
【発明が解決しようとする課題】しかしながら下水又は
排水再利用における色度測定法として一般に採用されて
いる前記白金・コバルト法とかJIS K 0102
(単色表示法)は、以下に記す理由により下水等の高度
処理監視,制御用として適していない。However, the above-mentioned platinum / cobalt method or JIS K 0102, which is generally adopted as a chromaticity measuring method in the reuse of sewage or waste water, is used.
The (single color display method) is not suitable for monitoring and controlling advanced treatment of sewage, etc. for the following reasons.
【0016】即ち、白金・コバルト法は肉眼での目視に
よる比色法であり、この目視を透過光量に置き換えるこ
とは可能であるが、色調の区別はできない。特に上水処
理では類黄色ないし黄褐色を評価すれば良いが、下水又
は排水再利用の場合には、可視光領域全般の範囲で色度
を評価する必要があるため、単なる比色だけでは不十分
であるものといえる。That is, the platinum-cobalt method is a colorimetric method by visual observation with the naked eye, and this visual observation can be replaced by the amount of transmitted light, but the color tone cannot be distinguished. Especially in clean water treatment, yellowish or yellowish brown color may be evaluated, but in the case of sewage or wastewater reuse, it is necessary to evaluate chromaticity in the entire visible light range, so mere colorimetry is not enough. It can be said that it is enough.
【0017】他方のJIS法(単色表示法)は、色調を
評価することができるが、可視光の400〜700nm
の範囲で20nm間隔でのデータが必要であるため、連
続的に測定するには装置が大型化してしまうという難点
がある。The other JIS method (monochromatic display method) can evaluate the color tone, but the visible light is 400 to 700 nm.
Since there is a need for data at intervals of 20 nm in the above range, there is a problem that the device becomes large in size for continuous measurement.
【0018】特に下水又は排水を高度処理システムによ
り修景用水・親水用水として利用するための監視・制御
用として採用する色度測定装置に求められる要件として
は、自動的且つ連続的な測定が可能であり、類黄色,黄
褐色以外の色調に対しても評価できることが挙げられ
る。又、オゾン処理等により高度処理された処理水は、
ほとんど類黄色ないし黄褐色であるが、監視・制御用と
しては高度処理前の色度も測定する必要があるため、他
の色調も評価することが要求される。染色排水が流入す
る場合は特に上記色調評価の必要性が高い。Especially, the chromaticity measuring device used for monitoring and controlling the use of sewage or wastewater as scenic water or hydrophilic water by an advanced treatment system requires automatic and continuous measurement. It is also possible to evaluate the color tone other than yellowish or yellowish brown. In addition, treated water that has been highly treated by ozone treatment, etc.
Although it is almost yellowish or yellowish brown, it is also necessary to evaluate other color tones because it is necessary to measure the chromaticity before advanced treatment for monitoring and control. When dyeing wastewater flows in, the above-mentioned color tone evaluation is highly necessary.
【0019】色度測定装置に求められる他の要件とし
て、前記白金・コバルト法による測定と相関性が高いこ
とが挙げられる。即ち、前記建設省から出された「下水
処理水の修景・親水利用水質検討マニュアル(案)」で
は白金・コバルト法を基本としているため、一般的な統
一性を考慮しても上記マニュアルに準拠し、相関性があ
ることが好ましいものと考えられる。Another requirement for the chromaticity measuring device is that it has a high correlation with the measurement by the platinum-cobalt method. In other words, the “Scenic Treatment Water Landscape / Hydrophilic Water Quality Study Manual (Draft)” issued by the Ministry of Construction is based on the platinum / cobalt method, so even if general uniformity is taken into consideration, Conformity and correlation are considered preferable.
【0020】そこで本発明は上記の問題点に鑑み、特に
自動的且つ連続的な測定を可能として下水等の高度処理
監視,制御用として適しており、しかも前記白金・コバ
ルト法による測定と相関性が高い下水又は排水処理にお
ける色度測定方法及び装置を提供することを目的とする
ものである。In view of the above problems, the present invention is particularly suitable for monitoring and controlling advanced treatment of sewage or the like, which enables automatic and continuous measurement, and has correlation with the measurement by the platinum-cobalt method. It is an object of the present invention to provide a method and an apparatus for measuring chromaticity in the treatment of sewage or waste water with high quality.
【0021】[0021]
【課題を解決するための手段】本発明は上記の目的を達
成するために、先ず請求項1により、試料水の波長39
0nm付近での吸光度を測定し、色度標準液で作成した
検量線から試料水の色度を算定した後、上記試料水につ
いて別途に可視光波長域内での一つ又は二つ以上の波長
での吸光度を測定して、測定された特定波長における吸
光度のピーク高さから前記試料水の色度を補正する色度
測定方法を提供する。In order to achieve the above object, the present invention firstly proposes a wavelength 39 of sample water according to claim 1.
After measuring the absorbance at around 0 nm and calculating the chromaticity of the sample water from the calibration curve prepared with the chromaticity standard solution, the sample water was separately measured at one or more wavelengths within the visible light wavelength range. And a chromaticity measurement method for correcting the chromaticity of the sample water from the measured peak height of the absorbance at a specific wavelength.
【0022】更に請求項2により、試料水が流入する測
定セルの一方に集光レンズを介在して配置された光源
と、該測定セルの他方に集光レンズを介在して配置され
た受光素子と、該受光素子と集光レンズとの間に配置さ
れ、2つ以上の波長から目的とする波長を選択する波長
選択フィルタと、選択された特定の波長における吸光度
を受光素子の受光データとして受け入れて、演算手段に
より色度値を算定し、且つ補正する演算及び制御信号出
力部とを具備して成る下水又は排水処理における色度測
定装置の構成にしてある。Further, according to the present invention, a light source arranged with a condenser lens in one of the measuring cells into which the sample water flows, and a light receiving element arranged with a condenser lens in the other of the measuring cells. And a wavelength selection filter arranged between the light receiving element and the condenser lens for selecting a target wavelength from two or more wavelengths, and the absorbance at the selected specific wavelength is received as light receiving data of the light receiving element. Then, the chromaticity measuring device in the sewage or wastewater treatment comprises a calculation and control signal output section for calculating and correcting the chromaticity value by the calculating means.
【0023】[0023]
【作用】かかる色度測定方法及び測定装置によれば、色
度を測定すべき試料水が測定セル内に入り、波長選択フ
ィルタによって予め設定された波長を選択してから光源
を点灯することにより、光源から発した光が集光レンズ
から測定セル内に入り、試料水を透過してから集光レン
ズ及び波長選択フィルタを介して受光素子に受け止めら
れ、選択された特定の波長における吸光度が受光素子の
受光データとして演算及び制御信号出力部に入力され
て、算定により色度値が測定される。According to such a chromaticity measuring method and measuring apparatus, the sample water whose chromaticity is to be measured enters the measuring cell, the wavelength preset by the wavelength selection filter is selected, and then the light source is turned on. , The light emitted from the light source enters the measuring cell through the condenser lens, passes through the sample water, and is received by the light receiving element through the condenser lens and the wavelength selection filter, and the absorbance at the selected specific wavelength is received. The light reception data of the device is input to the calculation and control signal output unit, and the chromaticity value is measured by calculation.
【0024】色度の測定は試料水の波長390nm付近
での吸光度を測定して色度標準液で作成した検量線から
試料水の色度を算定した後、同じ試料水について別の可
視光波長域内での一つ又は二つ以上の波長での吸光度を
測定して、測定された特定波長における吸光度のピーク
高さによって試料水の色度が補正される。The chromaticity is measured by measuring the absorbance of the sample water near the wavelength of 390 nm and calculating the chromaticity of the sample water from the calibration curve prepared with the chromaticity standard solution. The absorbance at one or more wavelengths in the region is measured, and the chromaticity of the sample water is corrected by the peak height of the absorbance at the measured specific wavelength.
【0025】[0025]
【実施例】以下図面に基づいて本発明にかかる色度測定
方法を適用した測定装置の具体的な実施例を説明する。
図1は色度自動測定装置の構成例を示す概要図であり、
図中の1は測定セルであって、この測定セル1の両側に
は集光レンズ2,3が配置されている。4は集光レンズ
2に近接して配置された光源,5は集光レンズ3に近接
して配置された受光素子,6は集光レンズ3と受光素子
5間に配置された波長選択フィルタ,7はステッピング
モータ,8は演算及び制御信号出力部,9は浮遊物除去
フィルタである。波長選択フィルタ6は2つ以上の波長
から目的とする波長を選択するために配置されている。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A specific embodiment of a measuring apparatus to which the chromaticity measuring method according to the present invention is applied will be described below with reference to the drawings.
FIG. 1 is a schematic diagram showing a configuration example of an automatic chromaticity measuring device,
Reference numeral 1 in the figure is a measuring cell, and condenser lenses 2 and 3 are arranged on both sides of the measuring cell 1. Reference numeral 4 is a light source arranged in the vicinity of the condenser lens 2, 5 is a light receiving element arranged in the vicinity of the condenser lens 3, 6 is a wavelength selection filter arranged between the condenser lens 3 and the light receiving element 5, Reference numeral 7 is a stepping motor, 8 is a calculation and control signal output unit, and 9 is a suspended matter removal filter. The wavelength selection filter 6 is arranged to select a target wavelength from two or more wavelengths.
【0026】これを具体的に述べると、詳細は後述する
ように、波長選択フィルタ6は波長390nm付近の吸
光度の測定を基本とし、可視光波長域内での一つ又は二
つ以上の波長での吸光度を測定するためのものである。More specifically, as will be described in detail later, the wavelength selection filter 6 is based on the measurement of the absorbance around the wavelength of 390 nm, and the wavelength selection filter 6 has one or more wavelengths within the visible light wavelength range. It is for measuring the absorbance.
【0027】かかる測定装置による色度測定時の操作概
要は以下の通りである。即ち色度を測定すべき試料水1
0は先ず浮遊物除去フィルタ9によって濾過された後、
管路11を経由して測定セル1の底壁側からセル内に入
る。この時に余分な試料水10はオーバーフロー管12
を介して溢流する。The outline of the operation when measuring the chromaticity by such a measuring device is as follows. That is, sample water 1 whose chromaticity should be measured
0 is first filtered by the suspended matter removal filter 9 and then
It enters into the cell from the bottom wall side of the measuring cell 1 via the conduit 11. At this time, excess sample water 10 is overflow pipe 12
Overflow through.
【0028】そしてステッピングモータ7の駆動により
波長選択フィルタ6を回転させ、この波長選択フィルタ
6により、予め設定された波長を選択してから光源4を
点灯する。これらステッピングモータ7の駆動及び光源
4の点灯は、演算及び制御信号出力部8の出力信号に基
づいて行われる。Then, the wavelength selection filter 6 is rotated by driving the stepping motor 7, and the wavelength selection filter 6 selects a preset wavelength and then turns on the light source 4. The driving of the stepping motor 7 and the lighting of the light source 4 are performed based on the output signal of the calculation and control signal output unit 8.
【0029】すると光源4から発した光が集光レンズ2
から測定セル1内に入り、試料水10を透過してから集
光レンズ3及び波長選択フィルタ6を介して受光素子5
に受け止められ、選択された特定の波長における吸光度
が受光素子5の受光データとして演算及び制御信号出力
部8に入力されて、以下に説明する測定原理に基づいて
色度値が算定される。Then, the light emitted from the light source 4 is condensed by the condenser lens 2.
From inside to the measurement cell 1 and through the sample water 10 and then through the condenser lens 3 and the wavelength selection filter 6 to the light receiving element 5
The light absorbency at the selected specific wavelength is input to the calculation and control signal output unit 8 as the light reception data of the light receiving element 5, and the chromaticity value is calculated based on the measurement principle described below.
【0030】以下に本実施例における色度測定の根拠と
なる各種データの解析結果を説明する。図2は前記上水
試験方法4.色度の項で規定された白金・コバルト法に
基づいて、各色度に調製された色度標準液について波長
390nmの吸光度(E390)を50mmセルで測定
した結果を示すグラフである。同図によれば色度と吸光
度は良い相関性を示し、色度標準液については吸光度
(E390)で色度を評価することができることが判明
した。The analysis results of various data which are the basis of the chromaticity measurement in this embodiment will be described below. FIG. 2 shows the water supply test method 4. It is a graph which shows the result of having measured the light absorbency (E390) of wavelength 390nm with a 50 mm cell about the chromaticity standard liquid prepared for each chromaticity based on the platinum-cobalt method prescribed | regulated by the term of chromaticity. According to the figure, the chromaticity and the absorbance show a good correlation, and it was found that the chromaticity can be evaluated by the absorbance (E390) for the chromaticity standard solution.
【0031】図3は実試料に対する前記白金・コバルト
法に基づく色度測定値と、色度標準液で作成した検量線
から試料水の色度を算定する前記透過光測定法に基づく
色度測定値とを比較したグラフであり、具体的に述べる
と、下水2次処理水を一定の条件でオゾン処理し、各オ
ゾン処理時間毎に試料水を採取して、一方は白金・コバ
ルト法(比色法)で、他方は図2のグラフを検量線とし
て波長390nmでの透過光測定法で測定した結果をそ
れぞれグラフ化して比較している。FIG. 3 shows a chromaticity measurement value based on the platinum-cobalt method for an actual sample and a chromaticity measurement based on the transmitted light measurement method for calculating the chromaticity of sample water from a calibration curve prepared with a chromaticity standard solution. It is a graph comparing with the value. Specifically, sewage secondary treated water is subjected to ozone treatment under constant conditions, sample water is sampled at each ozone treatment time, and one is platinum / cobalt method (ratio 2) using the graph of FIG. 2 as a calibration curve, and the other graphs the results measured by the transmitted light measuring method at a wavelength of 390 nm for comparison.
【0032】図3から上記両測定法の差は、低色度域,
例えば色度が5度以上でオゾン処理時間が20分以下の
時に大きいことが分かる。From FIG. 3, the difference between the above two measuring methods is that
For example, it can be seen that when the chromaticity is 5 degrees or more and the ozone treatment time is 20 minutes or less, it is large.
【0033】図4は上記に鑑みて図3と同じ実試料水に
ついてオゾン処理時間を20分以下とした時の波長35
0〜800nmの吸光度スペクトル(Abs)を示した
グラフである。又、図5は1度〜20度に調製した色度
標準液の波長350〜800nmの吸光度スペクトルを
示したグラフである。In view of the above, FIG. 4 shows a wavelength 35 when the ozone treatment time is 20 minutes or less for the same actual sample water as in FIG.
It is the graph which showed the light absorption spectrum (Abs) of 0-800 nm. Further, FIG. 5 is a graph showing an absorbance spectrum of a chromaticity standard solution prepared at 1 to 20 degrees at a wavelength of 350 to 800 nm.
【0034】図4と図5とを比較すると、色度標準液の
吸光度スペクトルでは、波長550nmよりも長波長側
での吸光度はほぼゼロであるのに対して、実試料水では
波長630nm付近に吸光度のピークMがあることが認
められる。このピークMは高色度域側で大きく、これが
図3で示した白金・コバルト法と透過光測定法での測定
色度差の原因と考えられる。Comparing FIG. 4 and FIG. 5, in the absorbance spectrum of the chromaticity standard solution, the absorbance on the longer wavelength side than the wavelength of 550 nm is almost zero, while in the actual sample water, the wavelength is around 630 nm. It can be seen that there is a peak M of absorbance. This peak M is large on the high chromaticity side, and this is considered to be the cause of the difference in measured chromaticity between the platinum-cobalt method and the transmitted light measurement method shown in FIG.
【0035】図6は図3における両測定法で測定した結
果の色度差と、図4における波長630nmでの吸光度
ピークMの高さの関係を示したグラフである。両者はほ
ぼ直線関係にあり、これに基づき図3に示した透過光測
定法の値を補正することができることが判明した。FIG. 6 is a graph showing the relationship between the difference in chromaticity as a result of measurement by both measurement methods in FIG. 3 and the height of the absorbance peak M at the wavelength of 630 nm in FIG. It was found that the two are in a substantially linear relationship, and based on this, the value of the transmitted light measurement method shown in FIG. 3 can be corrected.
【0036】上記に基づいて白金・コバルト法による色
度測定値と、透過光測定法により測定された色度を補正
した結果を図7のグラフに示す。図7によれば、白金・
コバルト法による色度測定結果と補正した透過光測定法
の色度値が良く一致していることが分かる。The graph of FIG. 7 shows the results of correcting the chromaticity measured by the platinum-cobalt method and the chromaticity measured by the transmitted light measuring method based on the above. According to FIG. 7, platinum
It can be seen that the chromaticity measurement result by the cobalt method and the chromaticity value by the corrected transmitted light measurement method are in good agreement.
【0037】上記の試料水は目視的にもオゾン処理前は
少し青みを帯びた淡黄色であったのが、処理時間20分
後には青みが消えて普通の淡黄色になったことが観察さ
れており、上記補正が合理的方法であることが確認され
た。It was observed visually that the above sample water was slightly bluish and pale yellow before the ozone treatment, but after 20 minutes of treatment, the bluish color disappeared to become a normal pale yellow. Therefore, it was confirmed that the above amendment is a rational method.
【0038】又、下水処理水は青み以外に赤み等も考え
られ、その場合には赤みに相当した波長での補正が有効
であると考えられる。従って本実施例における高度処理
システム監視・制御における色度測定の条件を満足する
方法として、波長390nm付近の吸光度(透過光率)
の測定を基本とし、可視光波長域内の別の一つ、又は二
つ以上の波長での吸光度を測定して補正する方法が最適
である。In addition to the bluish tint, the treated sewage water may have a reddish tint, and in that case, it is considered that correction at a wavelength corresponding to the reddish tint is effective. Therefore, as a method of satisfying the condition of chromaticity measurement in the monitoring and control of the advanced processing system in the present embodiment, the absorbance (transmitted light rate) around the wavelength of 390 nm is used.
The most suitable method is to measure the absorbance at another wavelength or two or more wavelengths in the visible light wavelength range and correct it based on the above measurement.
【0039】[0039]
【発明の効果】以上詳細に説明したように、本発明によ
れば色度を測定する試料水を測定セル内で波長選択フィ
ルタによって選択された波長に基づく光の透過と、選択
された特定の波長における受光素子の受光データに基づ
く吸光度から演算及び補正手段によって色度値を連続的
に測定することができる。特に下水又は排水再利用の場
合には上水処理とは異なって類黄色ないし黄褐色のみの
評価では不十分であり、可視光領域全般の範囲で色度を
評価するとともに色調の区別をすることが必要であるた
め、本発明にかかる測定方法は下水等の高度処理監視,
制御用として適している。As described in detail above, according to the present invention, the sample water whose chromaticity is to be measured transmits the light based on the wavelength selected by the wavelength selection filter in the measuring cell and the selected specific water. The chromaticity value can be continuously measured by the calculation and correction means from the absorbance based on the light reception data of the light receiving element at the wavelength. Especially in the case of reuse of sewage or waste water, unlike the treatment of tap water, it is not enough to evaluate only yellowish or yellowish brown, and it is necessary to evaluate the chromaticity in the entire visible light range and distinguish the color tone. Therefore, the measuring method according to the present invention requires monitoring of advanced treatment of sewage, etc.
Suitable for control.
【0040】更に従来の単に肉眼での目視による比色法
とは異なって客観的な測定が可能であり、可視光の40
0〜700nmの範囲での吸光度測定データを装置の大
型化を必要とせずに連続的に測定可能でしかも類黄色,
黄褐色以外の色調に対しても評価可能となり、下水等の
高度処理監視,制御用として求められる要件を満足して
おり、且つ白金・コバルト法による測定と相関性が高い
ので、一般的な統一性の面からも好ましい色度測定方法
及び装置を提供することができる。Further, objective measurement can be performed unlike the conventional colorimetric method by visual inspection with the naked eye.
Absorbance measurement data in the range of 0 to 700 nm can be continuously measured without increasing the size of the device, and it is yellowish.
Since it is possible to evaluate colors other than yellowish brown, it satisfies the requirements for monitoring and controlling advanced treatment of sewage, etc., and has a high correlation with the measurement by the platinum / cobalt method. It is possible to provide a chromaticity measuring method and apparatus that are also preferable from the viewpoint of sex.
【図1】本実施例にかかる色度測定装置の構成例を示す
概要図。FIG. 1 is a schematic diagram showing a configuration example of a chromaticity measuring device according to this embodiment.
【図2】色度標準液の波長390nmの吸光度(E39
0)を測定した結果を示すグラフ。FIG. 2 is the absorbance (E39) of a chromaticity standard solution at a wavelength of 390 nm.
The graph which shows the result of having measured 0).
【図3】実試料に対する白金・コバルト法に基づく色度
測定値と、透過光測定法に基づく色度測定値とを比較し
たグラフ。FIG. 3 is a graph comparing measured chromaticity values based on a platinum-cobalt method with actual samples and measured chromaticity values based on a transmitted light measurement method.
【図4】実試料についてオゾン処理時間に対する吸光度
スペクトルを示すグラフ。FIG. 4 is a graph showing an absorbance spectrum of an actual sample with respect to ozone treatment time.
【図5】色度標準液の吸光度スペクトルを示すグラフ。FIG. 5 is a graph showing an absorbance spectrum of a chromaticity standard solution.
【図6】白金・コバルト法と透過光測定法による色度差
と、波長630nmでの吸光度のピークの高さの関係を
示したグラフ。FIG. 6 is a graph showing the relationship between the chromaticity difference between the platinum-cobalt method and the transmitted light measurement method and the height of the peak of absorbance at a wavelength of 630 nm.
【図7】白金・コバルト法による色度測定値と、透過光
測定法により測定された色度を補正した結果を示すグラ
フ。FIG. 7 is a graph showing the chromaticity measurement value by the platinum-cobalt method and the result of correcting the chromaticity measured by the transmitted light measurement method.
1…測定セル 2,3…集光レンズ 4…光源 5…受光素子 6…波長選択フィルタ 7…ステッピングモータ 8…演算及び制御信号出力部 9…浮遊物除去フィルタ 10…試料水 12…オーバーフロー管 DESCRIPTION OF SYMBOLS 1 ... Measurement cell 2, 3 ... Condensing lens 4 ... Light source 5 ... Light receiving element 6 ... Wavelength selection filter 7 ... Stepping motor 8 ... Calculation and control signal output part 9 ... Floating matter removal filter 10 ... Sample water 12 ... Overflow tube
───────────────────────────────────────────────────── フロントページの続き (72)発明者 清水 公一 東京都品川区大崎2丁目1番17号 株式会 社明電舎内 ─────────────────────────────────────────────────── ─── Continued Front Page (72) Koichi Shimizu Inventor, Koichi Shimizu 2-1-117 Osaki, Shinagawa-ku, Tokyo
Claims (2)
を測定し、色度標準液で作成した検量線から試料水の色
度を算定した後、上記試料水について別途に可視光波長
域内での一つ又は二つ以上の波長での吸光度を測定し
て、測定された特定波長における吸光度のピーク高さか
ら前記試料水の色度を補正することを特徴とする下水又
は排水処理における色度測定方法。1. The absorbance of the sample water near a wavelength of 390 nm is measured, and the chromaticity of the sample water is calculated from a calibration curve prepared with a chromaticity standard solution. Then, the sample water is separately measured in the visible light wavelength range. Chromaticity measurement in sewage or wastewater treatment, characterized by measuring the absorbance at one or more wavelengths and correcting the chromaticity of the sample water from the peak height of the absorbance at the measured specific wavelength. Method.
レンズを介在して配置された光源と、該測定セルの他方
に集光レンズを介在して配置された受光素子と、該受光
素子と集光レンズとの間に配置され、2つ以上の波長か
ら目的とする波長を選択する波長選択フィルタと、選択
された特定の波長における吸光度を受光素子の受光デー
タとして受け入れて、演算手段により色度値を算定し、
且つ補正する演算及び制御信号出力部とを具備して成る
ことを特徴とする下水又は排水処理における色度測定装
置。2. A light source arranged with a condenser lens on one side of a measuring cell into which sample water flows, a light receiving element arranged on the other side of the measurement cell with a condenser lens, and the light receiving element. A wavelength selection filter which is arranged between the element and the condenser lens and which selects a target wavelength from two or more wavelengths, and the absorbance at the selected specific wavelength is received as the light reception data of the light receiving element, and the calculation means Calculate the chromaticity value by
A chromaticity measuring device in sewage or wastewater treatment, which comprises a calculation and control signal output unit for correction.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP33563093A JPH07198593A (en) | 1993-12-28 | 1993-12-28 | Chromaticity measuring method and apparatus in sewage or drain disposal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP33563093A JPH07198593A (en) | 1993-12-28 | 1993-12-28 | Chromaticity measuring method and apparatus in sewage or drain disposal |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH07198593A true JPH07198593A (en) | 1995-08-01 |
Family
ID=18290746
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP33563093A Pending JPH07198593A (en) | 1993-12-28 | 1993-12-28 | Chromaticity measuring method and apparatus in sewage or drain disposal |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07198593A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112285035A (en) * | 2020-11-23 | 2021-01-29 | 常州智腾环境科技有限公司 | Water color recognition device and water color recognition method |
-
1993
- 1993-12-28 JP JP33563093A patent/JPH07198593A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112285035A (en) * | 2020-11-23 | 2021-01-29 | 常州智腾环境科技有限公司 | Water color recognition device and water color recognition method |
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