JP6236874B2 - Anionic polymer concentration measuring method and apparatus - Google Patents

Anionic polymer concentration measuring method and apparatus Download PDF

Info

Publication number
JP6236874B2
JP6236874B2 JP2013109964A JP2013109964A JP6236874B2 JP 6236874 B2 JP6236874 B2 JP 6236874B2 JP 2013109964 A JP2013109964 A JP 2013109964A JP 2013109964 A JP2013109964 A JP 2013109964A JP 6236874 B2 JP6236874 B2 JP 6236874B2
Authority
JP
Japan
Prior art keywords
anionic polymer
concentration
measuring
cell
measurement
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.)
Active
Application number
JP2013109964A
Other languages
Japanese (ja)
Other versions
JP2014228467A (en
Inventor
信太郎 森
信太郎 森
幸祐 志村
幸祐 志村
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP2013109964A priority Critical patent/JP6236874B2/en
Publication of JP2014228467A publication Critical patent/JP2014228467A/en
Application granted granted Critical
Publication of JP6236874B2 publication Critical patent/JP6236874B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
  • Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)

Description

本発明は、冷却水系やボイラー等の蒸気発生設備を備える水系中に添加された水処理用アニオン性ポリマーの該水中における濃度を測定する方法及び装置に関する。   The present invention relates to a method and an apparatus for measuring the concentration of an anionic polymer for water treatment added to a water system equipped with a steam generating facility such as a cooling water system or a boiler.

冷却水系やボイラー等の蒸気発生設備を備える水系のスケール、腐食、及び汚れ防止等、水処理の目的のためにアクリル酸重合体、アクリル酸共重合体、マレイン酸重合体、マレイン酸共重合体等のアニオン性ポリマーが添加される。アニオン性ポリマーは高性能なスケール防止剤であるが、スケール防止能を十分に発揮させるためには、対象水系中のアニオン性ポリマーの濃度管理が極めて重要である。このようなアニオン性ポリマーの水中濃度を測定する方法として、特許文献1に、水系から検水を採取後、試薬を添加してアニオン性ポリマーと反応させて白濁を生じさせ、波長が400〜900nmのいずれかの可視光線を照射して比濁することができる持ち運び可能な測定装置を用いて測定する方法が記載されている(特許文献1の請求項1)。特許文献1では、この持ち運び可能な測定装置は、蓋付き測定セルと、前記測定セルを装着できる開口部と、該開口部の側面に設けられた可視光の照射部と、その透過光又は反射光を受ける受光部とからなる光学測定部と、該光学測定部を覆って遮光できる遮光キャップと、該光学測定部からの電気信号を受けて演算するデータ処理部と、データ処理部で得られた結果を表示する表示部から構成されている(同、請求項5)。   Acrylic polymer, acrylic acid copolymer, maleic acid polymer, maleic acid copolymer for water treatment purposes, such as water scale with corrosion generating equipment such as cooling water and boilers, corrosion and dirt prevention Anionic polymers such as are added. An anionic polymer is a high-performance scale inhibitor, but in order to fully exhibit the scale preventive ability, it is extremely important to control the concentration of the anionic polymer in the target aqueous system. As a method for measuring the concentration of such anionic polymer in water, Patent Document 1, after collecting sample water from an aqueous system, adding a reagent to react with the anionic polymer to cause white turbidity, and the wavelength is 400 to 900 nm. A method is described in which measurement is performed using a portable measuring device that can be turbidized by irradiation with any visible light (Claim 1 of Patent Document 1). In Patent Document 1, this portable measuring device includes a lidded measuring cell, an opening in which the measuring cell can be mounted, a visible light irradiation unit provided on a side surface of the opening, and transmitted light or reflected light. Obtained by an optical measurement unit comprising a light receiving unit that receives light, a light shielding cap that covers and covers the optical measurement unit, a data processing unit that receives and calculates an electrical signal from the optical measurement unit, and a data processing unit It is comprised from the display part which displays the result (same, Claim 5).

特開2006−38462JP 2006-38462 A

特許文献1に開示されたアニオン性ポリマーの測定方法においては、正確な測定を行うためには複数の試薬と検水の正確な量の分取が必要である。また、各操作間で行う攪拌が不十分な場合は、検水がアニオン性ポリマー成分を含んでいなくても、試薬同士が互いに高濃度で接触した結果、白濁を生じ、測定結果に正の誤差を与えることがあった。   In the method for measuring an anionic polymer disclosed in Patent Document 1, in order to perform an accurate measurement, it is necessary to collect an accurate amount of a plurality of reagents and sample water. In addition, if the stirring performed between each operation is insufficient, even if the sample water does not contain an anionic polymer component, the reagents come into contact with each other at a high concentration, resulting in white turbidity and positive measurement results. There was an error.

本発明は、水中のアニオン性ポリマーの濃度を容易かつ精度よく測定することができるアニオン性ポリマー濃度の測定方法及び装置を提供することを目的とする。   An object of this invention is to provide the measuring method and apparatus of an anionic polymer density | concentration which can measure the density | concentration of the anionic polymer in water easily and accurately.

本発明のアニオン性ポリマーの濃度測定方法は、水系中のアニオン性ポリマーの濃度を測定する方法であって、予めキレート剤の水溶液を封入した測定セルへ水系から採取した検水を注入後、第四級アンモニウム塩の水溶液を添加し、攪拌してアニオン性ポリマーと反応させて白濁を生じさせ、波長が400〜900nmのいずれかの可視光線の透過率又は吸光度を測定してアニオン性ポリマーの濃度を測定することを特徴とする。   The method for measuring the concentration of an anionic polymer of the present invention is a method for measuring the concentration of an anionic polymer in an aqueous system, and after injecting a sample collected from the aqueous system into a measurement cell in which an aqueous solution of a chelating agent is previously enclosed, Add an aqueous solution of a quaternary ammonium salt, stir to react with the anionic polymer to cause white turbidity, measure the transmittance or absorbance of any visible light having a wavelength of 400 to 900 nm, and measure the concentration of the anionic polymer Is measured.

アニオン性ポリマーとしては、アクリル酸系重合体又は共重合体、マレイン酸系重合体又は共重合体などが例示される。   Examples of the anionic polymer include an acrylic acid polymer or copolymer, a maleic acid polymer or copolymer, and the like.

本発明のアニオン性ポリマーの濃度測定装置は、予めキレート剤の水溶液を封入した測定セルと、該測定セルの吸光度又は透過率を測定する光学測定部と、該光学測定部からの信号を受けて演算するデータ処理部と、データ処理部で得られた結果を表示する表示部と、を含む持ち運び可能な、水系中におけるアニオン性ポリマーの濃度測定装置である。   An anionic polymer concentration measuring device of the present invention receives a measurement cell in which an aqueous solution of a chelating agent is encapsulated in advance, an optical measurement unit for measuring the absorbance or transmittance of the measurement cell, and a signal from the optical measurement unit. It is a portable anionic polymer concentration measuring device in an aqueous system, including a data processing unit for calculation and a display unit for displaying a result obtained by the data processing unit.

本発明では、予めキレート剤の水溶液を測定セルに封入してあるので、測定現場でセルに注入する操作は、検水の注入操作と、第四級アンモニウム塩の水溶液の注入操作の2操作だけとなる。このため、アニオン性ポリマーの濃度を容易に測定することができる。また、測定セルに規定濃度のキレート剤の水溶液を規定量封入しておくことにより、アニオン性ポリマーの濃度を精度よく測定することができる。   In the present invention, since the aqueous solution of the chelating agent is enclosed in the measurement cell in advance, the operation of injecting the cell into the cell at the measurement site is only two operations of the test water injection operation and the quaternary ammonium salt aqueous solution injection operation. It becomes. For this reason, the density | concentration of an anionic polymer can be measured easily. Moreover, the concentration of the anionic polymer can be accurately measured by enclosing a predetermined amount of an aqueous solution of a chelating agent having a specified concentration in the measurement cell.

実施例の測定結果を示すグラフである。It is a graph which shows the measurement result of an Example. 比較例の測定結果を示すグラフである。It is a graph which shows the measurement result of a comparative example.

本発明のアニオン性ポリマー濃度測定方法では、予めキレート剤の水溶液を封入した測定セルへ水系から採取した検水を注入後、第四級アンモニウム塩を添加し、攪拌してアニオン性ポリマーと反応させて白濁を生じさせ、波長が400〜900nmのいずれかの可視光線の透過率又は吸光度を測定してアニオン性ポリマーの濃度を測定する。   In the anionic polymer concentration measuring method of the present invention, after injecting a sample collected from an aqueous system into a measuring cell in which an aqueous solution of a chelating agent is encapsulated in advance, a quaternary ammonium salt is added and stirred to react with the anionic polymer. The concentration of the anionic polymer is measured by measuring the transmittance or absorbance of visible light having a wavelength of 400 to 900 nm.

本発明方法は、水中のアニオン性ポリマーが、第四級アンモニウム塩と反応し、定量的に水中に不溶性物質が生成し、試料水が白濁する現象を利用したものであり、その白濁の程度からアニオン性ポリマーの濃度を知ることに基礎を置いている。   The method of the present invention utilizes a phenomenon in which an anionic polymer in water reacts with a quaternary ammonium salt to quantitatively produce an insoluble substance in water, and the sample water becomes clouded. Based on knowing the concentration of anionic polymer.

本発明におけるアニオン性ポリマーは、分子中に複数のカルボキシル基、ないしスルホン酸基を有する分子量500以上の水溶性高分子化合物であり、水系における腐食防止、スケール防止を主たる目的に加えられているものである。アニオン性ポリマーの例としては、アクリル酸の単一又は共重合体、マレイン酸の単一又は共重合体、イタコン酸の単一又は共重合体、2−アクリルアミド−2−メチルプロパンスルホン酸の単一又は共重合体、アリルヒドロキシプロパンスルホン酸の単一又は共重合体等の1種又は2種以上が挙げられる。   The anionic polymer in the present invention is a water-soluble polymer compound having a molecular weight of 500 or more having a plurality of carboxyl groups or sulfonic acid groups in the molecule, and is added for the main purpose of preventing corrosion and preventing scale in aqueous systems. It is. Examples of anionic polymers include acrylic acid mono- or copolymers, maleic acid mono- or copolymers, itaconic acid mono- or copolymers, 2-acrylamido-2-methylpropanesulfonic acid mono- or copolymers. 1 type or 2 types or more, such as a mono- or copolymer, a mono- or copolymer of allyl hydroxypropane sulfonic acid, etc. are mentioned.

測定対象となる検水中のアニオン性ポリマー濃度は0.1〜500mg/L、特に1〜50mg/L程度が好適である。   The anionic polymer concentration in the test water to be measured is preferably about 0.1 to 500 mg / L, particularly about 1 to 50 mg / L.

測定対象とされる試料水は、アニオン性ポリマー以外に腐食防止、スケール防止、スライムコントロール剤等を含んでもよい。   The sample water to be measured may contain corrosion prevention, scale prevention, slime control agent and the like in addition to the anionic polymer.

本発明で用いるキレート剤は、試料水に共存する金属イオンが第四級アンモニウム塩とアニオン性高分子電解質との定量的反応を妨害するのをマスキングするとともに、第四級アンモニウム塩とアニオン性高分子電解質との沈殿反応に影響を及ぼし、アニオン性高分子電解質の高濃度域での検量線の直線性を確保するためのものである。キレート剤を塩として添加することにより反応時のpH緩衝剤として作用させることもできる。キレート剤としてはエチレンジアミン四酢酸塩(EDTA)、ニトリロ三酢酸塩、ジエチレントリアミン五酢酸塩等のアミノカルボン酸類、クエン酸塩、リンゴ酸塩、酒石酸塩、グリコール酸塩等のヒドロキシ酸類が使用できるが、これらは単独ないし2種以上組み合わせて使用してもよい。ここでいう塩とはナトリウム塩、カリウム塩、リチウム塩、アンモニウム塩、アミン塩等である。   The chelating agent used in the present invention masks the metal ions coexisting in the sample water from interfering with the quantitative reaction between the quaternary ammonium salt and the anionic polymer electrolyte, and the quaternary ammonium salt and the anionic high salt. This influences the precipitation reaction with the molecular electrolyte and ensures the linearity of the calibration curve in the high concentration region of the anionic polymer electrolyte. A chelating agent may be added as a salt to act as a pH buffer during the reaction. As chelating agents, aminocarboxylic acids such as ethylenediaminetetraacetate (EDTA), nitrilotriacetate, diethylenetriaminepentaacetate, and hydroxy acids such as citrate, malate, tartrate, glycolate can be used. These may be used alone or in combination of two or more. The salt here is sodium salt, potassium salt, lithium salt, ammonium salt, amine salt and the like.

セル内に封入するキレート剤水溶液の濃度は、100〜10000mg/L特に1000〜5000mg/L程度が好ましい。   The concentration of the chelating agent aqueous solution sealed in the cell is preferably about 100 to 10000 mg / L, particularly about 1000 to 5000 mg / L.

本発明では、キレート剤水溶液を封入しておくセルとしてはポリスチレン、ポリエチレン、ポリプロピレン、ポリメタクリル酸メチル、ポリカーボネートなどの合成樹脂製のものが好ましい。セルは、取り外し可能なシール蓋を備えており、測定に際してはこのシール蓋を取り外して検水等をセル中に添加することが好ましい。   In the present invention, a cell made of a synthetic resin such as polystyrene, polyethylene, polypropylene, polymethyl methacrylate, and polycarbonate is preferable as the cell in which the chelating agent aqueous solution is sealed. The cell is provided with a removable sealing lid, and it is preferable to remove the sealing lid and add test water or the like to the cell for measurement.

このような合成樹脂製セルとしては市販品を用いることができる。市販のセルとしては、ポリスチレン製、光路長10mm、光路幅10mm、高さ45mm、外幅12.5mmのものがある。このセルに1〜3mL程度のキレート剤水溶液を注入した後、ポリスチレン、ポリエチレン、ポリプロピレン、ポリメタクリル酸メチル、ポリカーボネートなどよりなる蓋をセル上端面にポリエステル製の熱接着フィルムによって気密に付着させてキレート剤水溶液を封入する。   A commercially available product can be used as such a synthetic resin cell. Commercially available cells include those made of polystyrene, having an optical path length of 10 mm, an optical path width of 10 mm, a height of 45 mm, and an outer width of 12.5 mm. After injecting 1 to 3 mL of chelating agent aqueous solution into this cell, a lid made of polystyrene, polyethylene, polypropylene, polymethyl methacrylate, polycarbonate, etc. is airtightly attached to the upper end surface of the cell with a polyester thermal adhesive film to chelate. Enclose the agent aqueous solution.

このセルに検水を注入する場合、注入後のセル内の水面高さが20〜40mmとなるように注入することが好ましい。   When injecting test water into this cell, it is preferable to inject it so that the water level in the cell after injection is 20 to 40 mm.

セルに検水を注入した後、第四級アンモニウム塩の水溶液をセルに添加する。本発明で用いる第四級アンモニウム塩は、アニオン性ポリマーと定量的に反応して安定な白濁を生じるものであればいかなるものでもよいが、好ましくは炭素数が12以上の第四級アンモニウム塩である。第四級アンモニウム塩の具体的な例として、テトラアルキルアンモニウム塩、トリアルキルベンジルアンモニウム塩、ジアルキルジベンジルアンモニウム塩、アルキルトリベンジルアンモニウム塩、ベンゼトニウム塩、ベンザルコニウム塩、アルキルピリジニウム塩、イミダゾリニウム塩ならびにこれらの誘導体である。第四級アンモニウム塩は分子中に第四級アンモニウム基が2個以上あってもよく、そのような化合物の例として、ポリ〔オキシエチレン(ジメチルイミノ)エチレン(ジメチルイミノ)エチレンジクロライド〕、ポリジアリルジアルキルアンモニウム塩、ポリ(メタ)アクリロイルオキシアルキルトリアルキルアンモニウム塩、ポリ(メタ)アクリルアミドアルキルトリアルキルアンモニウム塩等がある。また第四級アンモニウム塩の塩としては塩化物、臭化物、沃化物、硫酸塩等である。   After injecting test water into the cell, an aqueous solution of a quaternary ammonium salt is added to the cell. The quaternary ammonium salt used in the present invention may be any quaternary ammonium salt as long as it reacts quantitatively with an anionic polymer to produce a stable white turbidity, preferably a quaternary ammonium salt having 12 or more carbon atoms. is there. Specific examples of quaternary ammonium salts include tetraalkylammonium salts, trialkylbenzylammonium salts, dialkyldibenzylammonium salts, alkyltribenzylammonium salts, benzethonium salts, benzalkonium salts, alkylpyridinium salts, imidazolinium Salts as well as their derivatives. The quaternary ammonium salt may have two or more quaternary ammonium groups in the molecule. Examples of such a compound include poly [oxyethylene (dimethylimino) ethylene (dimethylimino) ethylene dichloride], polydiallyl. Examples include dialkylammonium salts, poly (meth) acryloyloxyalkyltrialkylammonium salts, poly (meth) acrylamide alkyltrialkylammonium salts, and the like. Examples of the quaternary ammonium salt include chloride, bromide, iodide, sulfate and the like.

セルに添加される第四級アンモニウム塩水溶液の濃度は1〜5000mg/L、特に100〜1000mg/L程度が好ましい。   The concentration of the aqueous quaternary ammonium salt solution added to the cell is preferably 1 to 5000 mg / L, particularly preferably about 100 to 1000 mg / L.

本発明で用いるのに好ましい測定装置は、予めキレート剤を封入した蓋付き測定セルと、前記測定セルを装着することができ、かつ、波長が400〜900nmのいずれかの可視光の照射部と、その透過光又は反射光を受ける受光部とからなる光学測定部と、該光学測定部を覆って遮光することができる遮光キャップと、該光学測定部からの電気信号を受けて演算するデータ処理部と、データ処理部で得られた結果を表示する表示部とを含む持ち運び可能なものである。   A preferable measuring device for use in the present invention is a measuring cell with a lid encapsulating a chelating agent in advance, a measuring cell with a wavelength of 400 to 900 nm, which can be equipped with the measuring cell, and a visible light irradiation unit. An optical measurement unit comprising a light receiving unit that receives the transmitted or reflected light, a light shielding cap that covers and covers the optical measurement unit, and data processing that receives and calculates an electrical signal from the optical measurement unit And a display unit for displaying the result obtained by the data processing unit.

水中のアニオン性ポリマーの濃度を測定したい水系に、この持ち運び可能なアニオン性ポリマー測定装置を持参し、対象水系から採取した検水を、キレート剤を封入した測定セルに注入する。検水の注入量は正確に測定する。   Bring this portable anionic polymer measuring device to the water system in which the concentration of the anionic polymer in the water is to be measured, and inject the sampled water collected from the target water system into the measuring cell in which the chelating agent is enclosed. Accurately measure the sample injection rate.

次に、該測定セルに第四級アンモニウム塩水溶液を添加し、撹拌する。この撹拌を行うには、セルに蓋を装着し、数回以上振るのが好ましい。   Next, an aqueous quaternary ammonium salt solution is added to the measurement cell and stirred. In order to perform this stirring, it is preferable to attach a lid to the cell and shake it several times.

アニオン性ポリマーと反応して安定な白濁を生じるに必要な量以上の第四級アンモニウム塩が添加されるように、第四級アンモニウム塩水溶液がセルに添加される。屋外での分析を行う場合には、数十μLの容量で滴下可能な点眼容器を用いることが好ましい。   An aqueous quaternary ammonium salt solution is added to the cell so that more quaternary ammonium salt is added than is necessary to react with the anionic polymer to produce a stable cloudiness. When analyzing outdoors, it is preferable to use an eye drop container that can be dropped in a volume of several tens of μL.

測定対象の比濁度がゼロ点補正を実施しなくても充分なSN比が得られるよう第四級アンモニウム塩水溶液濃度を選択しておけば、第四級アンモニウム塩の水溶液を滴下する前に、測定装置のゼロ補正を実施する必要はない。第四級アンモニウム塩水溶液を添加する前のキレート剤水溶液及び検水の特定波長の可視光の透過率又は吸光度を予め測定し、次いで、第四級アンモニウム塩水溶液を添加した後のセルの透過率又は吸光度を測定し、両者の差から、検水中のアニオン性ポリマーの濃度を算出することができる。   If the concentration of the quaternary ammonium salt aqueous solution is selected so that a sufficient SN ratio can be obtained even if the turbidity of the measurement target is not subjected to zero point correction, before dropping the aqueous solution of the quaternary ammonium salt, There is no need to perform zero correction of the measuring device. The transmittance or absorbance of the chelating agent aqueous solution and test water before adding the quaternary ammonium salt aqueous solution is measured in advance, and then the transmittance of the cell after adding the quaternary ammonium salt aqueous solution. Alternatively, the absorbance can be measured, and the concentration of the anionic polymer in the test water can be calculated from the difference between the two.

用いる波長は、白濁を精度良く捉えられるものならば、400〜900nmの間で任意に選択すれば良い。現在、特定化合物の測定を目的とした固定波長を用いたハンディタイプの簡易測定装置が市販されている。これらのうち、本発明では、残留塩素測定用に波長500〜550nmの可視光を使用した、HACH社製POCKET COLORIMETERIIを使用すれば、簡便に、かつ精度良く実施することができて好ましい。特にコンビナートの大規模水系では、通常スライムコントロール対策として塩素が使用されており、上記装置を用いた塩素濃度は頻繁に測定されている。従って、上記装置を使用すると、セルと試薬を変えるだけで、残留塩素濃度とアニオン性ポリマー濃度を測定することができ、極めて好都合である。   The wavelength to be used may be arbitrarily selected from 400 to 900 nm as long as the cloudiness can be accurately captured. Currently, a handy type simple measuring device using a fixed wavelength for the purpose of measuring a specific compound is commercially available. Of these, in the present invention, it is preferable to use POCKET COLORIMTER II manufactured by HACH, which uses visible light having a wavelength of 500 to 550 nm for residual chlorine measurement, because it can be carried out easily and accurately. Especially in the large-scale water system of a complex, chlorine is usually used as a slime control measure, and the chlorine concentration using the above apparatus is frequently measured. Therefore, when the above apparatus is used, the residual chlorine concentration and the anionic polymer concentration can be measured only by changing the cell and the reagent, which is very convenient.

本発明に係る測定装置の使用にあたっては、一般的な測定装置と同様に、予め、測定対象のアニオン性ポリマー標準品の濃度を変えて測定し、測定装置の出力(前記装置の場合、指示値と呼ばれる)を得、該アニオン性ポリマーと出力値との関係を表わす検量線を作成しておく。   When using the measuring apparatus according to the present invention, as in a general measuring apparatus, the concentration of the anionic polymer standard product to be measured is measured in advance, and the output of the measuring apparatus (in the case of the apparatus, the indicated value) A calibration curve representing the relationship between the anionic polymer and the output value is prepared.

なお、測定時の温度については、常温(10〜30℃程度)で良い。   In addition, about the temperature at the time of measurement, normal temperature (about 10-30 degreeC) may be sufficient.

検水中に、アニオン性ポリマーとの白濁反応に影響を与える多価フェノール等の化合物が共存する場合には、当該影響物質を酸化剤等を用いて分解し、影響をなくしてから、アニオン性ポリマー濃度を測定する。   When compounds such as polyphenols that affect the cloudiness reaction with an anionic polymer coexist in the sample water, the affected substance is decomposed using an oxidizing agent, etc. Measure the concentration.

[比較例1]
アニオン性ポリマーとしてポリアクリル酸ナトリウムを5,10,15,20mg/Lそれぞれ含むようにした検水を測定セル(ポリスチレン製、光路長10mm、光路幅10mm、高さ45mm、外幅12.5mm)に4mL採取した後、蓋をして数回振った。
[Comparative Example 1]
Sample water containing sodium polyacrylate 5,10,15,20mg / L as anionic polymer, measuring cell (made of polystyrene, optical path length 10mm, optical path width 10mm, height 45mm, outer width 12.5mm) After collecting 4 mL, it was capped and shaken several times.

次いで前記セルをHACH社製POCKET COLORIMETERIIに装着して遮光キャップで光学測定部全体を覆い、波長528nmの可視光を用いて1回目の照射を行ない、ゼロ補正した。次に、キャップを取り、前記セルを取り出して蓋を取り、その中にEDTAを2重量%含む試薬を2mLと、塩化ベンゼトニウムを0.1重量%含む試薬を4mLをそれぞれ加え、蓋をして数回振った。その後、前記装置の光学測定部に再装着し、遮光キャップで覆い、5分間静置して反応させた。その後波長528nmの可視光を照射して吸光度を測定した。測定装置の指示値とポリアクリル酸ナトリウム濃度とをグラフにプロットして検量線を作成した。結果を図2に示す。   Next, the cell was attached to a POCKET COLORIMTER II manufactured by HACH, and the entire optical measurement unit was covered with a light-shielding cap, and the first irradiation was performed using visible light having a wavelength of 528 nm, and zero correction was performed. Next, remove the cap, take out the cell, remove the lid, add 2 mL of a reagent containing 2% by weight of EDTA and 4 mL of a reagent containing 0.1% by weight of benzethonium chloride, and cover the lid. Shake several times. Then, it was reattached to the optical measurement part of the said apparatus, covered with the light-shielding cap, and left to react for 5 minutes. Thereafter, visible light having a wavelength of 528 nm was irradiated to measure the absorbance. A calibration curve was prepared by plotting the indicated value of the measuring apparatus and the polyacrylic acid sodium concentration on a graph. The results are shown in FIG.

[実施例1]
ポリスチレン製、光路長10mm、光路幅10mm、高さ45mm、外幅12.5mmの測定セルにEDTA0.7重量%水溶液1.5mLを封入したセルを用いて測定を行った。セルの蓋を取り、比較例1とそれぞれ同一濃度のポリアクリル酸ナトリウム水溶液よりなる検水を1mL添加した後、塩化ベンゼトニウム5重量%水溶液を約20μLスポイトで滴下した。それ以外は比較例1と同様にして測定を行い、測定装置指示値とポリアクリル酸ナトリウム濃度とをグラフにプロットして検量線を作成した。結果を図1に示す。
[Example 1]
The measurement was performed using a cell made of polystyrene, having an optical path length of 10 mm, an optical path width of 10 mm, a height of 45 mm, and an outer width of 12.5 mm, in which 1.5 mL of an EDTA 0.7% by weight aqueous solution was sealed. The lid of the cell was removed, and 1 mL of test water composed of an aqueous sodium polyacrylate solution having the same concentration as in Comparative Example 1 was added, and then a 5 wt% aqueous solution of benzethonium chloride was added dropwise with an about 20 μL dropper. Otherwise, the measurement was performed in the same manner as in Comparative Example 1, and a calibration curve was created by plotting the measurement apparatus instruction value and the sodium polyacrylate concentration on a graph. The results are shown in FIG.

比較例1では、検水と試薬2種類の合計3種類の溶液を採取して比色セルで混合する必要があるが、実施例1では、予めキレート剤水溶液を封入した比色セルに、検水と第四級アンモニウム塩水溶液を添加するだけであるので、秤量時に発生する採水量の不確かさが大幅に低減し、測定精度が向上する。また、測定操作も容易である。   In Comparative Example 1, it is necessary to collect a total of three types of solutions including test water and two types of reagents and mix them in a colorimetric cell. In Example 1, in a colorimetric cell in which a chelating agent aqueous solution is previously sealed, Since only water and a quaternary ammonium salt aqueous solution are added, the uncertainty of the amount of water collected during weighing is greatly reduced, and the measurement accuracy is improved. Also, the measurement operation is easy.

一般に、ゼロ点調整(バックグラウンド補正とも言う)を行う理由は、セルの個体差や汚れに起因するものとサンプル自身に起因するもの(バッファーの吸収や不溶物の影響など)を差し引くためである。実施例1は、工業的に製作した合成樹脂製セルを用いることで、セルの個体差や汚れの影響を取り除いている。   In general, the reason for zero adjustment (also referred to as background correction) is to subtract from cell differences and contamination and from the sample itself (buffer absorption, insoluble effects, etc.) . In Example 1, by using an industrially manufactured synthetic resin cell, the influence of individual cell differences and dirt are eliminated.

なお、実施例1で用いた、試薬を封入した比色セルに純水を加えたときの吸光度のバラツキは0.01未満であり、ゼロ点調整は不要であった。   The variation in absorbance when pure water was added to the colorimetric cell enclosing the reagent used in Example 1 was less than 0.01, and zero adjustment was unnecessary.

Claims (3)

水系中のアニオン性ポリマーの濃度を測定する方法であって、
予めキレート剤の水溶液を封入した測定セルへ水系から採取した検水を注入後、第四級アンモニウム塩の水溶液を添加し、攪拌してアニオン性ポリマーと反応させて白濁を生じさせ、波長が400〜900nmのいずれかの可視光線の透過率又は吸光度を測定してアニオン性ポリマーの濃度を測定することを特徴とするアニオン性ポリマーの濃度測定方法。
A method for measuring the concentration of an anionic polymer in an aqueous system,
After injecting test water sampled from the water system into a measurement cell in which an aqueous solution of a chelating agent is encapsulated in advance, an aqueous solution of a quaternary ammonium salt is added and stirred to react with an anionic polymer to produce white turbidity, and the wavelength is 400 A method for measuring the concentration of an anionic polymer, comprising measuring the transmittance or absorbance of visible light of any of ˜900 nm to measure the concentration of the anionic polymer.
アニオン性ポリマーがアクリル酸系重合体又は共重合体、マレイン酸系重合体又は共重合体からなる群から選ばれる少なくとも1種であることを特徴とする請求項1記載のアニオン性ポリマーの濃度測定方法。   The concentration measurement of an anionic polymer according to claim 1, wherein the anionic polymer is at least one selected from the group consisting of an acrylic acid polymer or copolymer, a maleic acid polymer or a copolymer. Method. 予めキレート剤を封入した測定セルと、
該測定セルの吸光度又は透過率を測定する光学測定部と、
該光学測定部からの信号を受けて演算するデータ処理部と、
該データ処理部で得られた結果を表示する表示部と、
を含む持ち運び可能な、水系中におけるアニオン性ポリマーの濃度測定装置。
A measurement cell encapsulating a chelating agent in advance;
An optical measurement unit for measuring the absorbance or transmittance of the measurement cell;
A data processing unit that receives and calculates a signal from the optical measurement unit;
A display unit for displaying the results obtained by the data processing unit;
A device for measuring the concentration of an anionic polymer in an aqueous system that is portable.
JP2013109964A 2013-05-24 2013-05-24 Anionic polymer concentration measuring method and apparatus Active JP6236874B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2013109964A JP6236874B2 (en) 2013-05-24 2013-05-24 Anionic polymer concentration measuring method and apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2013109964A JP6236874B2 (en) 2013-05-24 2013-05-24 Anionic polymer concentration measuring method and apparatus

Publications (2)

Publication Number Publication Date
JP2014228467A JP2014228467A (en) 2014-12-08
JP6236874B2 true JP6236874B2 (en) 2017-11-29

Family

ID=52128428

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2013109964A Active JP6236874B2 (en) 2013-05-24 2013-05-24 Anionic polymer concentration measuring method and apparatus

Country Status (1)

Country Link
JP (1) JP6236874B2 (en)

Family Cites Families (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5987366A (en) * 1982-11-11 1984-05-19 Shimadzu Corp Pretreatment kit for analyzing catecholamine
JPS6315161A (en) * 1986-07-07 1988-01-22 Terumo Corp Blood sampling tube for blood test
JPH11319885A (en) * 1998-05-18 1999-11-24 Hakuto Co Ltd On-stream monitor of treating agent concentration containing anionic polymer electrolyte in aqueous system and method for controlling treating agent injection rate using the same
JP2005156332A (en) * 2003-11-25 2005-06-16 Sefa Technology Kk Blood inspection method and evacuated blood sampling tube used for the same
JP3867718B2 (en) * 2004-07-16 2007-01-10 栗田工業株式会社 Method for measuring the concentration of anionic polymers for water treatment
JP2006038462A (en) * 2004-07-22 2006-02-09 Kurita Water Ind Ltd Method and instrument for measuring concentration of anionic polymer in water system
CN101443462A (en) * 2006-05-15 2009-05-27 北海道公立大学法人札幌医科大学 Method for detecting disease-related marker using gastric mucosal lavage fluid
JP4894445B2 (en) * 2006-10-10 2012-03-14 Jnc株式会社 Calcium quantification method and calcium quantification kit
JP2011092104A (en) * 2009-10-30 2011-05-12 Hitachi Engineering & Services Co Ltd Test method and test apparatus for microorganism or the like
JP5840120B2 (en) * 2010-03-03 2016-01-06 日本化薬株式会社 Detection device

Also Published As

Publication number Publication date
JP2014228467A (en) 2014-12-08

Similar Documents

Publication Publication Date Title
EP2162738B1 (en) Method for determination of polymer concentration in water systems
Biver et al. Direct determination of tellurium and its redox speciation at the low nanogram level in natural waters by catalytic cathodic stripping voltammetry
US9791427B2 (en) System and method for calculating concentration of water treatment chemical
US20170038358A1 (en) Concentration-factor measurement device, concentration-factor measurement method, and water-quality-index-value measurement method
CN101413894A (en) Iodine content on site rapid quantitative detection reagent in common salt added with iodine and preparation process thereof
CN103063726A (en) Detection method for chlorine ion content in lithium-ion battery electrolyte
CN107247046A (en) A kind of ammonia nitrogen detection method of low mercury salt
CN111458329B (en) Total chlorine and residual chlorine analysis method
CN109632777A (en) A kind of method of ammonia-nitrogen content in detection waste water
JP6236874B2 (en) Anionic polymer concentration measuring method and apparatus
CN106404998B (en) The detection method of Theil indices in a kind of high concentration of hydrogen tin oxide products
JP2016217741A (en) Apparatus and method for measuring concentration of dissolved component
CN104914093B (en) The method of testing of constant cadmium and zinc in tellurium-zincium-cadmium crystal
CN104914083A (en) Method for simultaneously detecting I<-> and Br<-> by adopting fluorescence silver nanoclusters and application thereof
Liu et al. Modifications of the curcumin method enabling precise and accurate measurement of seawater boron concentration
JP4784309B2 (en) Judgment method of heavy metal fixation effect
Amin Application of a triacetylcellulose membrane with immobilizated of 5-(2′, 4′-dimethylphenylazo)-6-hydroxypyrimidine-2, 4-dione for mercury determination in real samples
JP2006038462A (en) Method and instrument for measuring concentration of anionic polymer in water system
CN106918833B (en) Gamma-ray irradiation dose conversion method based on transcription factor IIIA
JP4793314B2 (en) Judgment method of heavy metal fixation effect
JP2006215014A (en) Scale inhibitor concentration measuring method and instrument
Kirishima et al. Determination of the phenolic-group capacities of humic substances by non-aqueous titration technique
CN102393417B (en) Analytical method for mercuric chloride
JPH10332595A (en) On-stream monitoring apparatus for concentration of treatment agent containing anionic polymer electrolyte in water system and control method for injection amount of treatment agent
CN107764863A (en) A kind of method that Accurate Determining can be carried out to content of fluoride in drinking water

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20160406

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20170222

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20170228

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20171003

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20171016

R150 Certificate of patent or registration of utility model

Ref document number: 6236874

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150