JP3297420B2 - Automatic component concentration measurement system - Google Patents
Automatic component concentration measurement systemInfo
- Publication number
- JP3297420B2 JP3297420B2 JP2000167996A JP2000167996A JP3297420B2 JP 3297420 B2 JP3297420 B2 JP 3297420B2 JP 2000167996 A JP2000167996 A JP 2000167996A JP 2000167996 A JP2000167996 A JP 2000167996A JP 3297420 B2 JP3297420 B2 JP 3297420B2
- Authority
- JP
- Japan
- Prior art keywords
- solution
- measurement
- concentration
- component concentration
- valve
- 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.)
- Expired - Fee Related
Links
- 238000005259 measurement Methods 0.000 title claims description 65
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 74
- 239000000243 solution Substances 0.000 claims description 52
- 239000012895 dilution Substances 0.000 claims description 36
- 238000010790 dilution Methods 0.000 claims description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 24
- 238000011088 calibration curve Methods 0.000 claims description 22
- 238000002835 absorbance Methods 0.000 claims description 18
- 239000012482 calibration solution Substances 0.000 claims description 17
- 238000000034 method Methods 0.000 claims description 13
- 239000012266 salt solution Substances 0.000 claims description 11
- 238000000862 absorption spectrum Methods 0.000 claims description 9
- 238000005406 washing Methods 0.000 claims description 9
- 238000007865 diluting Methods 0.000 claims description 8
- 238000004140 cleaning Methods 0.000 claims description 4
- 238000010521 absorption reaction Methods 0.000 claims description 3
- 238000004364 calculation method Methods 0.000 claims description 3
- 239000012898 sample dilution Substances 0.000 claims 1
- 239000011780 sodium chloride Substances 0.000 description 34
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 32
- 239000007788 liquid Substances 0.000 description 27
- 239000008399 tap water Substances 0.000 description 17
- 235000020679 tap water Nutrition 0.000 description 17
- 239000001103 potassium chloride Substances 0.000 description 13
- 235000011164 potassium chloride Nutrition 0.000 description 13
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 8
- 150000003839 salts Chemical class 0.000 description 5
- 238000005070 sampling Methods 0.000 description 5
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 4
- 238000004458 analytical method Methods 0.000 description 4
- 239000001110 calcium chloride Substances 0.000 description 4
- 229910001628 calcium chloride Inorganic materials 0.000 description 4
- 229910001629 magnesium chloride Inorganic materials 0.000 description 4
- 238000001556 precipitation Methods 0.000 description 4
- 238000001514 detection method Methods 0.000 description 3
- 238000007599 discharging Methods 0.000 description 3
- 230000014509 gene expression Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000011002 quantification Methods 0.000 description 2
- 238000001228 spectrum Methods 0.000 description 2
- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 241000723347 Cinnamomum Species 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 238000005102 attenuated total reflection Methods 0.000 description 1
- 235000017803 cinnamon Nutrition 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000611 regression analysis Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
Landscapes
- Automatic Analysis And Handling Materials Therefor (AREA)
- Investigating Or Analysing Materials By Optical Means (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、製塩工程における
せんごう缶の缶内液のような、高温度かつ高濃度の塩類
水溶液の成分濃度測定に関する技術である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technique for measuring the component concentration of a high-temperature and high-concentration aqueous salt solution such as a liquid in a canned can in a salt-making process.
【0002】[0002]
【従来の技術】製塩工程におけるせんごう缶の缶内液の
成分濃度測定は、塩製品の品質を制御、管理するために
重要であり、その測定手段として赤外線分光光度計を用
いる場合がある。せんごう缶外に赤外分光光度計の測定
部を設置し缶内液の成分濃度測定を行う場合、缶内液を
缶外に採取して測定を行う必要があり、缶内液の温度域
は40〜120℃と高温でかつ飽和濃度であるため、せんご
う缶外に缶内液を排出すると温度低下により内容成分の
析出が起こることから、せんごう缶内の缶内液の組成と
缶外に採取した缶内液の組成が異なり、正確に缶内液の
成分濃度を把握することが困難であった。2. Description of the Related Art In a salt-making process, the measurement of the component concentration of a liquid in a can of a cinnamon can is important for controlling and controlling the quality of a salt product. In some cases, an infrared spectrophotometer is used as a measuring means. When installing the measuring part of the infrared spectrophotometer outside the can and measuring the component concentration of the liquid in the can, it is necessary to collect the liquid inside the can and perform the measurement. Is a high temperature of 40 to 120 ° C and has a saturated concentration, and when the liquid in the can is discharged outside the can, the temperature drop causes precipitation of content components. The composition of the liquid in the can collected outside was different, and it was difficult to accurately grasp the component concentration of the liquid in the can.
【0003】また、せんごう缶内に赤外分光光度計の測
定部を挿入し、缶内液成分濃度測定を直接行う場合に
は、安定して精度の良い測定値を得るための定期的な検
量線校正の実施や、石膏等によるスケール付着を解消す
るための定期的な測定系内のメンテナンスが必要であ
り、この操作が非常に困難であることから、缶内液濃度
の直接測定は行うことができない。[0003] In addition, when a measuring part of an infrared spectrophotometer is inserted into a can, and the concentration of a liquid component in the can is directly measured, periodic measurement for obtaining a stable and accurate measurement value is required. It is necessary to perform calibration curve calibration and regular maintenance in the measuring system to eliminate scale adhesion due to gypsum, etc., and this operation is extremely difficult, so perform direct measurement of the liquid concentration in the can. Can not do.
【0004】さらに、従来の赤外分光光度計を用いた缶
内液成分濃度測定に用いる検量線は、各缶内液温度範囲
に適した検量線を作成しないと測定誤差が大きくなると
いった問題点や、安定して精度の良い測定値を得るため
の検量線校正法が確立されていないという問題点があっ
た。これらのことから、自動的、安定的に缶内液の成分
濃度測定を行うことはこれまで困難であった。Further, a calibration curve used for measuring the concentration of a liquid component in a can using a conventional infrared spectrophotometer has a problem that a measurement error increases unless a calibration curve suitable for each liquid temperature range in the can is created. In addition, there has been a problem that a calibration curve calibration method for stably obtaining accurate measurement values has not been established. For these reasons, it has been difficult to automatically and stably measure the component concentration of the liquid in the can.
【0005】[0005]
【発明が解決しようとする課題】常に安定して精度の良
い缶内液成分濃度測定を自動で行うことのできる成分濃
度自動測定システムを提供することを課題とする。SUMMARY OF THE INVENTION An object of the present invention is to provide a system for automatically measuring the concentration of a component in a can, which is always stable and accurate.
【0006】[0006]
【課題を解決するための手段】本発明の発明者は、赤外
分光光度計によるATR法(全反射減衰法)により、製塩
工程におけるせんごう缶の缶内液のように、高温度でか
つ高濃度の塩類水溶液を水で10/7倍に希釈すること
により調製した未飽和溶液を用いて、該塩類水溶液の成
分濃度測定が可能であることに着目し、本発明を完成す
るに至った。すなわち、本発明の課題を解決する手段は
下記のとおりである。Means for Solving the Problems The present inventor has proposed that the ATR method (attenuated total reflection method) using an infrared spectrophotometer can be used at a high temperature and at a high temperature, such as in a canned can in a salt making process. The present invention was completed by noting that it is possible to measure the component concentration of the aqueous salt solution using an unsaturated solution prepared by diluting a high-concentration aqueous salt solution 10 / 7-fold with water. . That is, means for solving the problems of the present invention are as follows.
【0007】(1)高温度かつ高濃度の塩類水溶液の成
分濃度を自動的に測定するシステムであって、測定液の
採取、希釈、および各流路の洗浄を行う手段を有する採
取‐希釈系、希釈した測定溶液およびバックグラウン
ド、校正溶液の測定、およびこれらの測定を一定温度で
行う手段、及び測定セルの洗浄を行う手段を有する測定
系、および採取‐希釈系、測定系を構成する各機器の制
御、測定データの入力、保存、演算を行う手段、および
システムの操作を行う手段を有する制御系からなる、成
分濃度自動測定システム、(2)高温度かつ高濃度の塩
類水溶液を水で希釈する希釈率が10/7以上であるこ
とを特徴とする(1)記載の成分濃度自動測定システ
ム、(3)高温度かつ高濃度の塩類水溶液の成分濃度を
自動的に測定するシステムにおいて、プローブ型または
フローセル型の赤外分光光度計を用いて赤外線吸収スペ
クトルを測定することを特徴とする(1)又は(2)に
記載の成分濃度自動測定システム、(4)高温度かつ高
濃度の塩類水溶液の成分濃度を自動的に測定するシステ
ムにおいて、温度範囲に対応した塩類水溶液の希釈溶液
を用いて、目的変数を成分濃度、説明変数を水の赤外線
吸収に起因する複数の波数における吸光度とした重回帰
法で作成した検量線を用いることを特徴とする(1)、
(2)、(3)のいずれかに記載の成分濃度自動測定シ
ステム。以下に、本発明の成分濃度自動測定システムの
実施例を示し、本発明をより詳細に説明する。(1) A system for automatically measuring the component concentration of a high-temperature and high-concentration aqueous salt solution, which is a collection-dilution system having means for collecting and diluting a measurement solution and washing each flow path , A measurement system having a measurement solution and a background, a measurement of a calibration solution, and a means for performing these measurements at a constant temperature, and a means for cleaning the measurement cell, and a collection-dilution system, each of which constitutes a measurement system. A component concentration automatic measurement system including a control system having means for controlling equipment, inputting, storing, and calculating measurement data, and a means for operating the system. (2) A high temperature and high concentration aqueous salt solution is treated with water. (1) The component concentration automatic measurement system according to (1), wherein the dilution ratio is 10/7 or more, and (3) the system that automatically measures the component concentration of a high temperature and high concentration salt aqueous solution. Wherein the infrared absorption spectrum is measured using a probe-type or flow-cell-type infrared spectrophotometer, wherein the component concentration automatic measurement system according to (1) or (2), In a system that automatically measures the component concentration of a high-concentration saline solution, the target variable is the component concentration, and the explanatory variable is a plurality of wave numbers caused by infrared absorption of water, using a dilute solution of the saline solution corresponding to the temperature range. (1) characterized by using a calibration curve created by multiple regression method with absorbance at
(2) The component concentration automatic measurement system according to any one of (3) and (3). Hereinafter, examples of the automatic component concentration measurement system of the present invention will be described, and the present invention will be described in more detail.
【0008】[0008]
【発明の実施の形態】〔実施例〕 希釈率の決定 本発明の成分濃度自動測定システムは、高温の缶内液の
内容成分が常温付近まで冷却しても析出しない濃度にま
で水で一定割合に希釈する希釈系を含む。希釈率を決定
するために求められる条件は、冷却時に内容成分の析出
が起こらないこと、赤外ATR法による成分濃度測定は濃
度が比較的高い溶液の測定に適しているため高い濃度を
保持できることの2点である。そこで、20℃および80℃
の缶内相当溶液を用いて、以下に示す方法により最適な
希釈率を決定した。DESCRIPTION OF THE PREFERRED EMBODIMENTS [Example] Determination of Dilution Rate The automatic component concentration measurement system of the present invention uses a constant rate of water to a concentration at which contents of a high-temperature in-tank solution do not precipitate even when cooled to around room temperature. Includes a dilution system for dilution to The conditions required to determine the dilution ratio are that no precipitation of content components occurs during cooling, and that component concentration measurement by the infrared ATR method is suitable for measurement of a solution with a relatively high concentration, so that a high concentration can be maintained. There are two points. So, 20 ℃ and 80 ℃
The optimal dilution rate was determined by the following method using the solution in the can.
【0009】なお、本発明において「希釈率」とは、元
の塩類水溶液に水を加えて希釈する場合の希釈倍率を示
したもので、例えば「希釈率を10/7」とは、元の塩
類溶液7部に水3部を加えて全体を10部とすることであ
る。まず、20℃缶内液相当溶液の塩化カルシウム、塩化
マグネシウムおよび塩化カリウムの各成分濃度の分析値
を説明変数とし、塩化ナトリウム濃度の分析値を目的変
数として重回帰分析により解析を行うことにより20℃に
おける塩化ナトリウム濃度の予測式((1)式)を作成し
た。In the present invention, the term "dilution ratio" indicates a dilution ratio when water is added to an original salt solution to dilute the salt solution. 3 parts of water is added to 7 parts of the salt solution to make the whole 10 parts. First, the analysis value of each component concentration of calcium chloride, magnesium chloride, and potassium chloride in the solution corresponding to the solution in the 20 ° C can was used as an explanatory variable, and the analysis value of the sodium chloride concentration was used as an objective variable to perform analysis by multiple regression analysis. A prediction formula (equation (1)) for the concentration of sodium chloride at ° C was prepared.
【0010】[0010]
【数1】 C20pr (NaCl)=27.19−0.97 C20(CaCl2)−1.06 C20(MgCl2)−0.74 C20(KCl)・・・(1 ) C20pr(NaCl): 20℃における塩化ナトリウム濃度の予測
値/% C20(x):20℃におけるxの成分濃度の分析値/%(x=CaC
l2,MgCl2,KCl) 次に、80℃缶内液相当溶液の塩化カルシウム、塩化マグ
ネシウム、塩化カリウムおよび塩化ナトリウムの各成分
濃度の分析値から希釈率 を10/7、10/8、10
/9、1とした場合の各成分濃度の計算値を算出した
((2)式〜(5)式)。C 20pr (NaCl) = 27.19−0.97 C 20 (CaCl 2 ) −1.06 C 20 (MgCl 2 ) −0.74 C 20 (KCl) ・ ・ ・ (1) C 20pr (NaCl): chloride at 20 ° C. Predicted value of sodium concentration /% C 20 (x): Analyzed value of component concentration of x at 20 ° C./% (x = CaC
l 2 , MgCl 2 , KCl) Next, the dilution ratio was determined to be 10/7, 10/8, 10/10 from the analytical value of the component concentrations of calcium chloride, magnesium chloride, potassium chloride and sodium chloride in the solution corresponding to the solution in the 80 ° C can.
The calculated value of each component concentration was calculated assuming / 9 and 1.
(Equations (2) to (5)).
【0011】[0011]
【数2】 (Equation 2)
【0012】[0012]
【数3】 (Equation 3)
【0013】[0013]
【数4】 (Equation 4)
【0014】[0014]
【数5】 (Equation 5)
【0015】ここで、20℃における塩化ナトリウム濃度
の予測式((1)式)に、各希釈率における塩化カルシウ
ム、塩化マグネシウムおよび塩化カリウムの各成分濃度
の計算値を代入し、20℃相当の塩化ナトリウム濃度の予
測値を求め((6)式)、この予測値C’20pr(NaCl)と各希釈
率における塩化ナトリウム濃度の計算値Ccal(NaCl)との
比較を行った。Here, the calculated values of the concentration of each component of calcium chloride, magnesium chloride and potassium chloride at each dilution rate are substituted into the prediction formula of sodium chloride concentration at 20 ° C. (formula (1)), and The predicted value of the sodium chloride concentration was determined (Equation (6)), and the predicted value C ′ 20pr (NaCl) was compared with the calculated value C cal (NaCl) of the sodium chloride concentration at each dilution ratio.
【0016】[0016]
【数6】 C’20pr(NaCl)=27.19−0.97Ccal(CaCl2)−1.06Ccal(MgCl2)−0.74 Ccal(KCl)・・( 6) C’20pr(NaCl): 20℃における塩化ナトリウム濃度の予
測値/% この塩化ナトリウム濃度の予測値C’20pr(NaCl)は、80
℃の缶内液相当溶液を各希釈率で希釈したときの成分組
成において20℃に冷却したときの飽和塩化ナトリウム濃
度を、計算値Ccal(NaCl)は80℃缶内液相当溶液を各希釈
率で希釈したときに含まれる塩化ナトリウム濃度を示し
ている。(7)式に塩化ナトリウム濃度の予測値に対する
計算値の割合Rを示す。[6] C '20pr (NaCl) = 27.19-0.97C cal (CaCl 2) -1.06C cal (MgCl 2) -0.74 C cal (KCl) ·· (6) C' 20pr (NaCl): at 20 ° C. Predicted value of sodium chloride concentration /% The predicted value of sodium chloride concentration C ′ 20pr (NaCl) is 80
The saturated sodium chloride concentration when cooled to 20 ° C in the component composition when the solution corresponding to the solution in the can at ℃ is diluted at each dilution ratio, and the calculated value C cal (NaCl) is the dilution of the solution corresponding to the solution in the can at 80 ° C The figure shows the concentration of sodium chloride contained when diluted at a specific rate. Equation (7) shows the ratio R of the calculated value to the predicted value of the sodium chloride concentration.
【0017】[0017]
【数7】 R:塩化ナトリウム濃度の予測値に対する計算値の割合/
% 図1に塩化ナトリウム濃度の予測値に対する計算値の割
合Rと無希釈80℃缶内相当溶液の塩化ナトリウム濃度の
分析値との関係を示す。Rが100を越える場合、その溶液
の内容成分は結晶として析出することが予測される。し
たがって、80℃缶内液相当溶液が20℃においても析出を
起こさない希釈率は10/7以上であることから、本発
明の成分濃度自動測定システムでは希釈率を10/7以
上とした。(Equation 7) R: Ratio of calculated value to predicted value of sodium chloride concentration /
% Fig. 1 shows the relationship between the ratio R of the calculated value to the predicted value of the sodium chloride concentration and the analytical value of the sodium chloride concentration of the solution in the undiluted 80 ° C can. When R exceeds 100, the components of the solution are expected to precipitate as crystals. Therefore, since the dilution ratio at which the solution equivalent to the 80 ° C. can solution does not cause precipitation even at 20 ° C. is 10/7 or more, the dilution ratio is set to 10/7 or more in the automatic component concentration measurement system of the present invention.
【0018】成分濃度自動測定システム 図2に、本発明の成分濃度自動測定システムの概要を示
す。本システムは、缶内液の採取および希釈を行う採取
-希釈系1、希釈溶液の赤外線吸収スペクトルを測定する
測定系2、ポンプ、バルブ、測定機器の制御、測定デー
タの取り込み、吸光度差測定値、吸光度差校正値、成分
濃度算出および校正係数の計算、保存を行うコンピュー
タおよび制御盤を持つ制御系3で構成されている。FIG. 2 shows an outline of the automatic component concentration measuring system of the present invention. This system collects and dilutes the liquid in the can.
-Dilution system 1, measurement system 2 for measuring infrared absorption spectrum of diluted solution, control of pumps, valves, measuring instruments, acquisition of measurement data, absorbance difference measurement value, absorbance difference calibration value, component concentration calculation and calculation of calibration coefficient And a control system 3 having a computer for storing and a control panel.
【0019】なお、製塩工程に適用する場合、採取ライ
ンaはせんごう缶の管路に、洗浄ラインbは洗浄水の管
路に、希釈ラインcおよび水供給ラインdは水道水の管
路に、校正ラインe1,e2は校正溶液の管路にそれぞれ接
続される。以下のシステムフローチャートは缶内液の定
量を行うための測定ルーチンと缶内液の成分濃度の定量
に用いる検量線を2点の校正溶液により校正するための
校正ルーチンから成る。When applied to the salt-making process, the sampling line a is connected to a pipe of a sandbag, the washing line b is connected to a washing water pipe, and the dilution line c and the water supply line d are connected to a tap water pipe. And the calibration lines e1 and e2 are connected to the pipelines of the calibration solution, respectively. The following system flowchart comprises a measurement routine for quantifying the liquid in the can and a calibration routine for calibrating the calibration curve used for quantifying the component concentration of the liquid in the can with two calibration solutions.
【0020】a)測定ルーチン 採取-希釈系1において、まず、バルブV1、バルブV3およ
びバルブV5を開け、ポンプP1を作動し、採取ラインaか
ら缶内液S1を排出後、バルブV5を閉じ、バルブV4、バル
ブV7を開け、缶内液S1を希釈セルC1に仮導入する。次
に、バルブV7を閉じ、缶内液S1を希釈セルC1に本導入す
る。液面レベル計L1の検知部Sw1を検知後、バルブV1、
バルブV3およびバルブV4を閉め、ポンプP1を停止し、バ
ルブV6を開け、希釈ラインcから水道水W1を希釈セルC1
に導入する。さらに、液面レベル計L1の検知部Sw2の検
知後、バルブV6を閉じ、攪拌機A1を作動し、希釈溶液の
調製を行う。A) Measurement Routine In the sampling-dilution system 1, first, the valve V1, the valve V3, and the valve V5 are opened, the pump P1 is operated, the can solution S1 is discharged from the sampling line a, and the valve V5 is closed. The valves V4 and V7 are opened, and the in-can solution S1 is temporarily introduced into the dilution cell C1. Next, the valve V7 is closed, and the in-can solution S1 is fully introduced into the dilution cell C1. After detecting the detection part Sw1 of the liquid level meter L1, the valve V1,
Close the valves V3 and V4, stop the pump P1, open the valve V6, and add tap water W1 from the dilution line c to the dilution cell C1.
To be introduced. Further, after detecting the detection unit Sw2 of the liquid level meter L1, the valve V6 is closed, and the stirrer A1 is operated to prepare a diluted solution.
【0021】測定系2において、攪拌機A2を作動し、バ
ルブV8を開け、水供給ラインdから水道水W2を測定セルC
2に仮導入し、一定時間後にバルブV8を閉じ、バルブV9
を開け、水道水を排出する。さらに、バルブV9を閉じ、
バルブV8を開け、水供給ラインdから水道水W2を測定セ
ルC2に本導入する。測定セルC2に導入された水道水の温
度が恒温槽F1により一定になるまで待機後、攪拌機A2を
停止し、赤外分光光度計I1によりバックグラウンドスペ
クトルを測定する。測定後、バルブV9を開け、水道水の
排出を行った後、バルブV9を閉じる。次に、ポンプP2、
攪拌機A2を作動し、採取-希釈系において調製された希
釈溶液を測定セルC2に仮導入し、一定時間後、ポンプP2
を停止し、バルブV9を開け、希釈溶液の排出を行う。In the measuring system 2, the stirrer A2 is operated, the valve V8 is opened, and the tap water W2 is supplied from the water supply line d to the measuring cell C.
Temporarily introduced to 2 and after a certain period of time, close valve V8 and close valve V9
Open and drain tap water. In addition, close valve V9,
The valve V8 is opened, and the tap water W2 is fully introduced into the measurement cell C2 from the water supply line d. After waiting until the temperature of the tap water introduced into the measurement cell C2 becomes constant in the constant temperature bath F1, the stirrer A2 is stopped, and the background spectrum is measured by the infrared spectrophotometer I1. After the measurement, the valve V9 is opened, and after tap water is discharged, the valve V9 is closed. Next, pump P2,
Activate the stirrer A2 and temporarily introduce the diluted solution prepared in the collection-dilution system into the measurement cell C2, and after a certain time, pump P2
Is stopped, the valve V9 is opened, and the diluted solution is discharged.
【0022】さらに、ポンプP2を作動し、バルブV9を閉
じ、希釈溶液の本導入を行い、測定セルC2を満たした後
ポンプP2を停止する。測定セルC2に導入された希釈溶液
の温度が恒温槽F1により一定になるまで待機後、攪拌機
A2を停止し、赤外分光光度計I1により赤外線吸収スペク
トルを測定する。測定後、バルブV9を開け、希釈溶液を
排出する。排出後、バルブV9を閉じ、バルブV8を開け、
攪拌機A2を作動し、水供給ラインdから水道水W2を導入
し、一定時間後バルブV8を閉じ、測定セルC2の洗浄を行
う。洗浄後、バルブV9を開け、攪拌機A2を停止し、水道
水の排出を行う。Further, the pump P2 is operated, the valve V9 is closed, the diluted solution is fully introduced, and after filling the measuring cell C2, the pump P2 is stopped. After waiting until the temperature of the diluted solution introduced into the measurement cell C2 becomes constant in the constant temperature bath F1, the stirrer
Stop A2 and measure the infrared absorption spectrum with the infrared spectrophotometer I1. After the measurement, the valve V9 is opened and the diluted solution is discharged. After discharging, close valve V9, open valve V8,
The stirrer A2 is operated to introduce tap water W2 from the water supply line d, and after a certain time, the valve V8 is closed, and the measuring cell C2 is washed. After washing, the valve V9 is opened, the stirrer A2 is stopped, and tap water is discharged.
【0023】一方、希釈溶液を測定セルC2に本導入終了
後、採取-希釈系1において、バルブV2、バルブV3、バル
ブV4、バルブV5、バルブV7を開け、ポンプP1を作動し、
洗浄ラインbから洗浄水B1を導入し、排出側の採取ライ
ンaの洗浄を行う。さらに、バルブV3、バルブV4、バル
ブV5、バルブV7を閉じ、ポンプP1を停止し、バルブV1を
開け、洗浄ラインbからの洗浄水B1を導入し、せんごう
缶側の採取ラインaを洗浄する。On the other hand, after the introduction of the diluted solution into the measuring cell C2, the valve V2, the valve V3, the valve V4, the valve V5, and the valve V7 are opened in the sampling-dilution system 1, and the pump P1 is operated.
The washing water B1 is introduced from the washing line b, and the sampling line a on the discharge side is washed. Further, the valve V3, the valve V4, the valve V5, and the valve V7 are closed, the pump P1 is stopped, the valve V1 is opened, the washing water B1 from the washing line b is introduced, and the sampling line a on the side of the sandbag can is washed. .
【0024】制御系3においては、コンピュータD1およ
び制御盤E1により前記の測定ルーチンに従い、一連のバ
ルブ、ポンプの制御、測定機器の制御を行い、コンピュ
ータD1により赤外線吸収スペクトルの取り込みを行い、
後述のに示す6組の波数の吸光度差を求め、この吸光
度差を後述の-b)において算出した校正係数を用いて
補正し、補正した吸光度差を用いて各成分濃度と吸光度
差についての関係式により各成分濃度を算出し、これら
測定データの保存を行う。In the control system 3, a computer D1 and a control panel E1 control a series of valves and pumps and control measuring instruments in accordance with the above-mentioned measurement routine, and a computer D1 captures an infrared absorption spectrum.
The absorbance difference of the six wave numbers shown below is determined, the absorbance difference is corrected using the calibration coefficient calculated in -b) described below, and the relationship between each component concentration and the absorbance difference is calculated using the corrected absorbance difference. The concentration of each component is calculated by the formula, and the measured data is stored.
【0025】b)校正ルーチン 測定系2において、攪拌機A2を作動し、バルブV8を開
け、水供給ラインdから水道水W2を測定セルC2に仮導入
し、一定時間後にバルブV8を閉じ、バルブV9を開け、水
道水を排出する。さらに、バルブV9を閉じ、バルブV8を
開け、水供給ラインdから水道水W2を測定セルC2に本導
入する。測定セルC2に導入された水道水の温度が恒温槽
F1により一定になるまで待機後、攪拌機A2を停止し、赤
外分光光度計I1によりバックグラウンドスペクトルを測
定する。測定後、バルブV9を開け、水道水の排出を行っ
た後、バルブV9を閉じる。B) Calibration Routine In the measurement system 2, the stirrer A2 is operated, the valve V8 is opened, and tap water W2 is temporarily introduced into the measurement cell C2 from the water supply line d. After a certain time, the valve V8 is closed, and the valve V9 is closed. Open and drain tap water. Further, the valve V9 is closed, the valve V8 is opened, and the tap water W2 is fully introduced into the measuring cell C2 from the water supply line d. The temperature of tap water introduced into measurement cell C2 is
After waiting until it becomes constant by F1, the stirrer A2 is stopped, and the background spectrum is measured by the infrared spectrophotometer I1. After the measurement, the valve V9 is opened, and after tap water is discharged, the valve V9 is closed.
【0026】次に、バルブV10を開け、攪拌機A2を作動
し、校正ラインe1から校正溶液STD1を測定セルC2に仮導
入し、一定時間後バルブV10を閉じ、バルブV9を開け、
校正溶液STD1の排出を行う。さらに、バルブV9を閉じ、
バルブV10を開け、校正ラインe1から校正溶液STD1の本
導入を行う。バルブV10を閉じ、測定セルC2に導入され
た校正溶液STD1の温度が恒温槽F1により一定になるまで
待機後、攪拌機A2を停止し、赤外分光光度計I1により赤
外線吸収スペクトルを測定する。測定後、バルブV9を開
け、校正溶液STD1を排出する。排出後、バルブV11を開
け、攪拌機A2を作動し、校正ラインe2から校正溶液STD2
を測定セルC2に仮導入し、一定時間後、バルブV11を閉
じ、バルブV9を開け、校正溶液STD2の排出を行う。Next, the valve V10 is opened, the stirrer A2 is operated, and the calibration solution STD1 is temporarily introduced into the measuring cell C2 from the calibration line e1, and after a certain time, the valve V10 is closed and the valve V9 is opened.
Drain calibration solution STD1. In addition, close valve V9,
The valve V10 is opened, and the calibration solution STD1 is fully introduced from the calibration line e1. After closing the valve V10 and waiting until the temperature of the calibration solution STD1 introduced into the measurement cell C2 becomes constant in the thermostatic bath F1, the stirrer A2 is stopped, and the infrared absorption spectrum is measured by the infrared spectrophotometer I1. After the measurement, the valve V9 is opened, and the calibration solution STD1 is discharged. After discharging, open the valve V11, operate the stirrer A2, and perform the calibration solution STD2 from the calibration line e2.
Is temporarily introduced into the measurement cell C2, and after a certain time, the valve V11 is closed, the valve V9 is opened, and the calibration solution STD2 is discharged.
【0027】さらに、バルブV9を閉じ、バルブV11を開
け、校正ラインe2から校正溶液STD2の本導入を行う。バ
ルブV11を閉じ、測定セルC2に導入された校正溶液STD2
の温度が恒温槽F1により一定になるまで待機後、攪拌機
A2を停止し、赤外分光光度計I1により赤外線吸収スペク
トルを測定する。測定後、バルブV9を開け、校正溶液ST
D2を排出する。排出後、バルブV9を閉じ、バルブV8を開
け、攪拌機A2を作動し、水供給ラインdから水道水W2を
導入し、一定時間後バルブV8を閉じ、測定セルC2の洗浄
を行う。バルブV9を開け、攪拌機A2を停止し、水道水の
排出を行う。Further, the valve V9 is closed, the valve V11 is opened, and the calibration solution STD2 is introduced from the calibration line e2. The valve V11 is closed, and the calibration solution STD2 introduced into the measurement cell C2
After waiting until the temperature of the
Stop A2 and measure the infrared absorption spectrum with the infrared spectrophotometer I1. After the measurement, open the valve V9 and set the calibration solution ST
Emit D2. After discharging, the valve V9 is closed, the valve V8 is opened, the stirrer A2 is operated, tap water W2 is introduced from the water supply line d, and after a certain period of time, the valve V8 is closed and the measuring cell C2 is washed. Open valve V9, stop stirrer A2, and discharge tap water.
【0028】制御系においては、コンピュータD1および
制御盤E1により前記の校正ルーチンに従い、一連のバル
ブ、ポンプの制御、測定機器の制御を行い、コンピュー
タD1により各校正溶液の赤外線吸収スペクトルの取り込
みを行い、後述のに示す6組の波数の吸光度差を求
め、この吸光度差を用いて検量線校正についての関係式
により校正係数の算出し、これら校正データの保存を行
う。In the control system, the computer D1 and the control panel E1 control a series of valves and pumps and control the measuring equipment in accordance with the above-mentioned calibration routine, and the computer D1 takes in the infrared absorption spectrum of each calibration solution. Then, the absorbance differences of the six wave numbers shown below are determined, and the calibration coefficients are calculated by the relational expression for calibration curve calibration using the absorbance differences, and the calibration data is stored.
【0029】成分濃度測定に用いる検量線の作成 缶内液の塩化カルシウム、塩化マグネシウム、塩化カリ
ウムおよび塩化ナトリウムの各成分濃度(C(x))は、目
的変数を成分濃度、説明変数を水の吸収に起因する表1
に記載の6組の波数の吸光度差(測定波数と参照波数の
差)(Ak:k=1〜6 (kは表1の波数組の番号に対応))とした
(8)式の重回帰式により算出することができる。Preparation of Calibration Curve Used for Measurement of Component Concentration The concentration of each component (C (x)) of calcium chloride, magnesium chloride, potassium chloride and sodium chloride in the liquid in the can is calculated by using the objective variable as the component concentration and the explanatory variable as water. Table 1 due to absorption
Absorbance difference (difference between measured wave number and reference wave number) of 6 sets of wave numbers described in (A k : k = 1 to 6 (k corresponds to the number of wave number set in Table 1))
It can be calculated by the multiple regression equation of equation (8).
【0030】[0030]
【数8】 C(x)=α0(x)+α1(x)A1+α2(x)A2+α3(x)A3+α4(x)A4+α5 (x)A5+α6(x)A6 …(8) Ak:各波数の吸光度差(k=1〜6) C(x):xの成分濃度/%(x:CaCl2,MgCl2,KCl,NaCl) αm(x):定数(x:CaCl2, MgCl2, KCl, NaCl, m=0〜6)C (x) = α 0 (x) + α 1 (x) A 1 + α 2 (x) A 2 + α 3 (x) A 3 + α 4 (x) A 4 + α 5 (x) A 5 + α 6 (x) A 6 ... (8) Ak : Absorbance difference of each wave number (k = 1 to 6) C (x): Concentration /% of x (x: CaCl 2 , MgCl 2 , KCl, NaCl) α m (x): constant (x: CaCl 2 , MgCl 2 , KCl, NaCl, m = 0 to 6)
【0031】[0031]
【表1】 【table 1】
【0032】本発明の成分濃度自動測定システムにおい
ては缶内液温度に依存しない検量線を作成するため、広
い温度範囲の検量線用の希釈溶液を用いて検量線を作成
した。検量線は90点の20,40,60,80℃の缶内液相当溶液
を水で10/7倍に希釈した希釈溶液を用いて20℃で吸
光度差を測定し、(8)式の係数αm(x) (x:CaCl2,MgCl2,K
Cl,NaCl, m=0〜6)を決定することにより作成した。(9)
式〜(12)式に各成分濃度測定に用いる検量線を示す。In the automatic component concentration measuring system of the present invention, a calibration curve was prepared using a diluting solution for a calibration curve in a wide temperature range in order to prepare a calibration curve independent of the liquid temperature in the can. The calibration curve was obtained by measuring the difference in absorbance at 20 ° C using a dilute solution obtained by diluting 90 points of the solution in the can at 20,40,60,80 ° C with water 10/7 times. The coefficient of equation (8) α m (x) (x: CaCl 2 , MgCl 2 , K
Cl, NaCl, m = 0-6). (9)
Equations (12) show calibration curves used for measuring the concentration of each component.
【0033】[0033]
【数9】 C(CaCl2)= 5.30-3.40A1+1.58A2+621.34A3-47.99A4+46.27A5+203.50A6 …(9)## EQU9 ## C (CaCl 2 ) = 5.30-3.40A 1 + 1.58A 2 + 621.34A 3 -47.99A 4 + 46.27A 5 + 203.50A 6 … (9)
【0034】[0034]
【数10】 C(MgCl2)= 0.23-13.93A1+1.28A2-271.69A3+49.41A4+23.37A5-70.99A6 …(10 )C (MgCl 2 ) = 0.23-13.93A 1 + 1.28A 2 -271.69A 3 + 49.41A 4 + 23.37A 5 -70.99A 6 … (10)
【0035】[0035]
【数11】 C(KCl)= 17.85-25.63A1+10.66A2-143.48A3-223.71A4-289.05A5+183.59A6 …(11 )C (KCl) = 17.85-25.63A 1 + 10.66A 2 -143.48A 3 -223.71A 4 -289.05A 5 + 183.59A 6 … (11)
【0036】[0036]
【数12】 C(NaCl)=-16.53+21.24A1-12.71A2-582.26A3+135.44A4+234.15A5-229.73A6 …(12 ) Ak:各波数の吸光度差(k=1〜6) C(x):xの成分濃度の予測値/% (x:CaCl2,MgCl2,KCl,Na
Cl) 缶内液の定量 前記において作成した検量線の有効性について示す。
缶内液を水で10/7倍に希釈した缶内液希釈溶液を用
いて20℃で赤外線吸収スペクトルを測定し、得られた吸
光度差(A’k)を用いて検量線((9)式〜(12)式)に代入
し、缶内液の定量を行った((13)式〜(16)式)。C (NaCl) =-16.53 + 21.24A 1 -12.71A 2 -582.26A 3 + 135.44A 4 + 234.15A 5 -229.73A 6 … (12) A k : Absorbance difference of each wave number (k = 1-6) C (x): predicted value /% of component concentration of x (x: CaCl 2 , MgCl 2 , KCl, Na
Cl) Quantification of can solution The effectiveness of the calibration curve created above is shown below.
An infrared absorption spectrum was measured at 20 ° C. using a diluted solution of the in-can solution 10 / 7-fold with water at 20 ° C., and a calibration curve was obtained using the obtained absorbance difference (A ′ k ) ((9) The liquid in the can was quantitatively determined by substituting into the equations (Equations to (12)) (Equations (13) to (16)).
【0037】[0037]
【数13】 Cpr(CaCl2)= 5.30-3.40A’1+1.58A’2+621.34A’3-47.99A’4+46.27A’5+203.50 A’6 …(13)C pr (CaCl 2 ) = 5.30-3.40A ′ 1 + 1.58A ′ 2 + 621.34A ′ 3 −47.99A ′ 4 + 46.27A ′ 5 +203.50 A ′ 6 … (13)
【0038】[0038]
【数14】 Cpr(MgCl2)= 0.23-13.93A’1+1.28A’2-271.69A’3+49.41A’4+23.37A’5-70.99 A’6 …(14)C pr (MgCl 2 ) = 0.23-13.93A ′ 1 + 1.28A ′ 2 −271.69A ′ 3 + 49.41A ′ 4 + 23.37A ′ 5 −70.99 A ′ 6 … (14)
【0039】[0039]
【数15】 Cpr(KCl)= 17.85-25.63A’1+10.66A’2-143.48A’3-223.71A’4-289.05A’5+183 .59A’6 …(15)## EQU15 ## C pr (KCl) = 17.85-25.63A ' 1 + 10.66A' 2 -143.48A ' 3 -223.71A' 4 -289.05A ' 5 +183 .59A' 6 ... (15)
【0040】[0040]
【数16】 Cpr(NaCl)=-16.53+21.24A’1-12.71A’2-582.26A’3+135.44A’4+234.15A’5-22 9.73A’6 …(16) A’k:缶内液希釈溶液の各波数の吸光度差(k=1〜6) Cpr(x):xの成分濃度の測定値/% (x:CaCl2,MgCl2,KCl,
NaCl) 比較のために、60℃の缶内液相当溶液を水で10/7倍
に希釈した希釈溶液24点を用いて前記と同様に検量線
((17)式〜(20)式)を作成し、缶内液の定量を行った((2
1)式〜(24)式)。C pr (NaCl) =-16.53 + 21.24A ′ 1 -12.71A ′ 2 −582.26A ′ 3 + 135.44A ′ 4 + 234.15A ′ 5 -22 9.73A ′ 6 … (16) A ′ k : Absorbance difference of each wave number of solution in can solution (k = 1 to 6) C pr (x): Measured value of x component concentration /% (x: CaCl 2 , MgCl 2 , KCl,
(NaCl) For comparison, a calibration curve was prepared in the same manner as above using 24 dilute solutions obtained by diluting a solution equivalent to the solution in the can at 60 ° C 10/7 times with water.
(Equations (17) to (20)) were prepared, and the liquid in the can was quantified ((2
Expressions 1) to (24)).
【0041】[0041]
【数17】 C(CaCl2)= 19.21-9.32A1+0.83A2+1362.84A3-57.95A4+28.67A5+240.74A6 …(17 )(17) C (CaCl 2 ) = 19.21-9.32A 1 + 0.83A 2 + 1362.84A 3 -57.95A 4 + 28.67A 5 + 240.74A 6 … (17)
【0042】[0042]
【数18】 C(MgCl2)=-10.04-9.80A1+1.86A2-888.02A3+38.17A4+37.10A5-132.44A6 …(18 )(18) C (MgCl 2 ) =-10.04-9.80A 1 + 1.86A 2 -888.02A 3 + 38.17A 4 + 37.10A 5 -132.44A 6 … (18)
【0043】[0043]
【数19】 C(KCl)=12.16-43.25A1+6.97A2-324.94A3-116.28A4-340.10A5+26.29A6 …(19)(19) C (KCl) = 12.16-43.25A 1 + 6.97A 2 -324.94A 3 -116.28A 4 -340.10A 5 + 26.29A 6 ... (19)
【0044】[0044]
【数20】 C(NaCl)=-18.38+44.45A1-9.49A2-674.48A3+93.53A4+299.74A5-54.23A6 …(20) Ak:各波数の吸光度差(k=1〜6) C(x):xの成分濃度の予測値/%(x:CaCl2,MgCl2,KCl,NaCl)C (NaCl) =-18.38 + 44.45A 1 -9.49A 2 -674.48A 3 + 93.53A 4 + 299.74A 5 -54.23A 6 … (20) A k : Absorbance difference of each wave number (k = 1~6) C (x): predicted value of the component concentration of x /% (x: CaCl 2 , MgCl 2, KCl, NaCl)
【0045】[0045]
【数21】 Cpr(CaCl2)=19.21-9.32A’1+0.83A’2+1362.84A’3-57.95A’4+28.67A’5+240.7 4A’6 …(21)## EQU21 ## C pr (CaCl 2 ) = 19.21-9.32A ′ 1 + 0.83A ′ 2 + 1362.84A ′ 3 -57.95A ′ 4 + 28.67A ′ 5 +240.7 4A ′ 6 …(twenty one)
【0046】[0046]
【数22】 Cpr(MgCl2)=-10.04-9.80A’1+1.86A’2-888.02A’3+38.17A’4+37.10A’5-132.4 4A’6 …(22)C pr (MgCl 2 ) =-10.04-9.80A ′ 1 + 1.86A ′ 2 -888.02A ′ 3 + 38.17A ′ 4 + 37.10A ′ 5 -132.4 4A ′ 6 …(twenty two)
【0047】[0047]
【数23】 Cpr(KCl)=12.16-43.25A’1+6.97A’2-324.94A’3-116.28A’4-340.10A’5+26.29 A’6 …(23)## EQU23 ## C pr (KCl) = 11.66-43.25A ' 1 + 6.97A' 2 -324.94A ' 3 -116.28A' 4 -340.10A ' 5 +26.29 A' 6 … (23)
【0048】[0048]
【数24】 Cpr(NaCl)=-18.38+44.45A’1-9.49A’2-674.48A’3+93.53A’4+299.74A’5-54.2 3A’6 …(24) A’k:缶内液希釈溶液の各波数の吸光度差(k=1〜6) Cpr(x):xの成分濃度の測定値/% (x:CaCl2,MgCl2,KCl,
NaCl) 測定値の精度評価には平均自乗予測誤差MSEPを用いた。
(25)式にその定義を示す。C pr (NaCl) = − 18.38 + 44.45A ′ 1 −9.49A ′ 2 −674.48A ′ 3 + 93.53A ′ 4 + 299.74A ′ 5 −54.2 3A ′ 6 … (24) A ′ k : Absorbance difference of each wave number of the solution dilution solution in the can (k = 1 to 6) C pr (x): Measurement value /% of component concentration of x (x: CaCl 2 , MgCl 2 , KCl,
The mean squared prediction error MSEP was used to evaluate the accuracy of the measured values of NaCl).
Equation (25) shows the definition.
【0049】[0049]
【数25】 MSEP:平均自乗予測誤差 N:試料数 Cpr(x): xの成分濃度の測定値/%(x:CaCl2,MgCl2,KCl,Na
Cl) Cact(x): xの成分濃度の分析値/%(x:CaCl2,MgCl2,KCl,N
aCl)(Equation 25) MSEP: Mean square prediction error N: Number of samples C pr (x): Measurement value /% of component concentration of x (x: CaCl 2 , MgCl 2 , KCl, Na
Cl) C act (x): Analytical value of x component concentration /% (x: CaCl 2 , MgCl 2 , KCl, N
aCl)
【0050】表2に20〜80℃の検量線および60℃の検量
線を用いてそれぞれ缶内液を定量した時の各成分濃度の
測定値の平均自乗予測誤差を示す。いずれの成分につい
ても60℃の検量線を用いた場合と比較して20〜80℃の検
量線を用いた場合の方が予測誤差は小さかった。これ
は、製塩工程におけるせんごう缶の缶内液のような高濃
度の塩類水溶液においては、その温度により成分の飽和
度が異なり、これを10/7倍に希釈して未飽和とする
ことで飽和度の影響を平準化したことの効果である。し
たがって本発明に基づき、広い温度範囲の缶内液相当溶
液を希釈した希釈溶液を用いて検量線作成することによ
り、缶内液の測定値の缶内液温度依存性を解消すること
ができ、十分な精度で定量が可能であった。Table 2 shows the mean square prediction error of the measured value of each component concentration when the liquid in the can was quantified using the calibration curve at 20 to 80 ° C. and the calibration curve at 60 ° C. For all the components, the prediction error was smaller when the calibration curve at 20 to 80 ° C was used than when the calibration curve at 60 ° C was used. This is because, in a high-concentration aqueous salt solution such as the liquid in a canned can in the salt-making process, the degree of saturation of the component varies depending on the temperature, and this is diluted by a factor of 10 to make it unsaturated. This is the effect of equalizing the influence of the degree of saturation. Therefore, based on the present invention, by creating a calibration curve using a dilute solution obtained by diluting a solution corresponding to the in-can solution in a wide temperature range, it is possible to eliminate the in-can solution temperature dependency of the measured value of the in-can solution, Quantification was possible with sufficient accuracy.
【0051】[0051]
【表2】 [Table 2]
【0052】[0052]
【発明の効果】本発明の成分濃度自動測定システムは、
せんごう缶外に缶内液を排出しても缶内液採取時および
成分濃度測定時において内容成分の析出が起こらず、検
量線および検量線校正法を持ち、常に安定した缶内液成
分濃度測定を自動で行うことができる自動測定システム
であり、製塩工程の自動化、省力化およびコスト削減に
大きく貢献できる。The system for automatically measuring the concentration of components according to the present invention comprises:
Even if the liquid in the can is discharged out of the can, no precipitation of the contents occurs when collecting the liquid in the can or when measuring the component concentration. It is an automatic measurement system that can perform measurement automatically, and can greatly contribute to automation of salt production process, labor saving and cost reduction.
【図1】 塩化ナトリウム濃度の予測値に対する計算値
の割合Rと無希釈80℃缶内相当溶液の塩化ナトリウム濃
度の分析値との関係を示す図である。 ○:10/7倍希釈、□:10/8倍希釈、△:10/9
倍希釈、◇:無希釈FIG. 1 is a graph showing a relationship between a ratio R of a calculated value to a predicted value of a sodium chloride concentration and an analysis value of a sodium chloride concentration of a solution in an undiluted 80 ° C. can. ○: 10/7 dilution, □: 10/8 dilution, Δ: 10/9
Double dilution, ◇: No dilution
【図2】 本発明の実施例の製塩工程における成分濃度
自動測定システムの概要図である。FIG. 2 is a schematic diagram of a system for automatically measuring a component concentration in a salt production process according to an embodiment of the present invention.
1・・・採取-希釈系、2・・・測定系、3・・・制御系、V1〜V11・・
・バルブ、P1,P2・・・ポンプ、A1,A2・・・攪拌機、C1・・・希釈
セル、C2・・・測定セル、D1・・・コンピュータ、E1・・・制御
盤、F1・・・恒温槽、L1・・・液面レベル計、Sw1,Sw2・・・検知
部、I1・・・赤外分光光度計、a・・・採取ライン、b・・・洗浄
ライン、c・・・希釈ライン、d・・・水供給ライン、e1,e2・・・
校正溶液ライン S1・・・缶内液、B1・・・洗浄水、W1,W2・・・水道水、STD1,STD
2・・・校正溶液1 ・ ・ ・ Sampling-dilution system, 2 ・ ・ ・ Measurement system, 3 ・ ・ ・ Control system, V1 ~ V11 ...
・ Valve, P1, P2 ・ ・ ・ Pump, A1, A2 ・ ・ ・ Stirrer, C1 ・ ・ ・ Dilution cell, C2 ・ ・ ・ Measurement cell, D1 ・ ・ ・ Computer, E1 ・ ・ ・ Control panel, F1 ・ ・ ・Constant temperature bath, L1: liquid level meter, Sw1, Sw2: detection unit, I1: infrared spectrophotometer, a: sampling line, b: cleaning line, c: dilution Line, d ... water supply line, e1, e2 ...
Calibration solution line S1: Liquid in can, B1: Cleaning water, W1, W2: Tap water, STD1, STD
2 ・ ・ ・ Calibration solution
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI G01N 35/00 G01N 35/00 E 35/10 35/06 K (58)調査した分野(Int.Cl.7,DB名) G01N 35/08 G01N 21/27 G01N 21/35 G01N 33/00 G01N 35/00 G01N 35/10 JICSTファイル(JOIS)──────────────────────────────────────────────────の Continuation of the front page (51) Int.Cl. 7 identification code FI G01N 35/00 G01N 35/00 E 35/10 35/06 K (58) Field surveyed (Int.Cl. 7 , DB name) G01N 35/08 G01N 21/27 G01N 21/35 G01N 33/00 G01N 35/00 G01N 35/10 JICST file (JOIS)
Claims (4)
度を自動的に測定するシステムであって、測定液の採
取、希釈、および各流路の洗浄を行う手段を有する採取
‐希釈系、希釈した測定溶液およびバックグラウンド、
校正溶液の測定、およびこれらの測定を一定温度で行う
手段、および測定セルの洗浄を行う手段を有する測定
系、および採取‐希釈系、測定系を構成する各機器の制
御、測定データの入力、保存、演算を行う手段、および
システムの操作を行う手段を有する制御系からなる、成
分濃度自動測定システム。1. A system for automatically measuring the component concentration of a high-temperature and high-concentration aqueous salt solution, comprising a sample-dilution system having means for collecting and diluting a measurement solution and washing each channel, Diluted measurement solution and background,
Measurement of calibration solution, and means for performing these measurements at a constant temperature, and a measurement system having means for cleaning the measurement cell, and collection-dilution system, control of each device constituting the measurement system, input of measurement data, An automatic component concentration measurement system comprising a control system having means for performing storage and calculation, and means for operating the system.
釈する希釈率が10/7以上であることを特徴とする請
求項1記載の成分濃度自動測定システム。2. The component concentration automatic measurement system according to claim 1, wherein a dilution ratio of diluting a high temperature and high concentration aqueous salt solution with water is 10/7 or more.
度を自動的に測定するシステムにおいて、プローブ型ま
たはフローセル型の赤外分光光度計を用いて赤外線吸収
スペクトルを測定することを特徴とする請求項1又は2
に記載の成分濃度自動測定システム。3. A system for automatically measuring the component concentration of a high-temperature and high-concentration saline solution, wherein an infrared absorption spectrum is measured using a probe-type or flow-cell-type infrared spectrophotometer. Claim 1 or 2
The automatic component concentration measurement system according to 1.
度を自動的に測定するシステムにおいて、温度範囲に対
応した塩類水溶液の希釈溶液を用いて、目的変数を成分
濃度、説明変数を水の赤外線吸収に起因する複数の波数
における吸光度とした重回帰法で作成した検量線を用い
ることを特徴とする請求項1、2又は3のいずれかに記
載の成分濃度自動測定システム。4. A system for automatically measuring the component concentration of a high-temperature and high-concentration saline solution, wherein the objective variable is the component concentration and the explanatory variable is water, using a dilute solution of the saline solution corresponding to the temperature range. 4. The automatic component concentration measurement system according to claim 1, wherein a calibration curve created by a multiple regression method using absorbance at a plurality of wave numbers caused by infrared absorption is used.
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