JP2003194798A - Method for determining a small amount of environmentally polluting substance and kit for determination used therefor - Google Patents

Method for determining a small amount of environmentally polluting substance and kit for determination used therefor

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Publication number
JP2003194798A
JP2003194798A JP2001398541A JP2001398541A JP2003194798A JP 2003194798 A JP2003194798 A JP 2003194798A JP 2001398541 A JP2001398541 A JP 2001398541A JP 2001398541 A JP2001398541 A JP 2001398541A JP 2003194798 A JP2003194798 A JP 2003194798A
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JP
Japan
Prior art keywords
hydrophobic
temperature
trace
polymer compound
solid
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.)
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Application number
JP2001398541A
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Japanese (ja)
Other versions
JP3623777B2 (en
Inventor
Chiyo Matsubara
チヨ 松原
Hiroshi Yoshioka
浩 吉岡
Fumi Ninomiya
扶実 二宮
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PATENT CAPITAL Inc
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PATENT CAPITAL Inc
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  • Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for easily and accurately determining an extremely small amount of components, especially heavy metal ions, causing environmental pollution. <P>SOLUTION: A heat-reversible heat-sensitive high-molecular compound of a fine-fiber-like solid which is hydrophilic at low temperatures and hydrophobic at high temperatures is added to a supernatant liquid of the extremely small amount of pollutants, dissolved, and heated to a transition temperature or more to form solid matter and separate a liquid part. The solid heat-sensitive high- molecular compound encloses a hydrophobic coloring reagent which comes into reaction with the extremely small amount of pollutants and is colored. A solid part made of the heat-sensitive high-molecular compound mixed at temperatures lower than the transition temperature, heated to the transition temperatures or higher, enclosing a colored compound generated by the reaction between the extremely small amount of pollutants and the coloring reagent, and deposited is separated from the liquid part, dissolved in water or a solvent to measure its absorbance, or calorimetrically determined with a standard item. <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、新規な環境汚染微
量物質の定量方法及びそれに用いる定量用キットに関す
るものである。
TECHNICAL FIELD The present invention relates to a novel method for quantifying a trace amount of environmental pollutants and a quantification kit used therefor.

【0002】[0002]

【従来の技術】近年、環境汚染防止の観点から、大気
中、水中あるいは土壌中の極微量成分を定量することが
必要とされる機会が多くなってきているため、これらの
極微量成分を簡便かつ精度よく定量する方法に対する要
求が高まっている。このような微量成分の分析法の1つ
として、重金属イオンに対す比色定量法がある。これ
は、被分析物質と発色試薬とを反応させ、得られる反応
生成物を予備濃縮したのち、分光分析を行う方法であ
り、マイクログラムオーダーの定量が可能であるため、
広い分野において利用されている。
2. Description of the Related Art In recent years, from the viewpoint of preventing environmental pollution, it has become necessary to quantify very small amounts of components in the air, water or soil. In addition, there is an increasing demand for a method of accurately quantifying. As one of the analysis methods for such trace components, there is a colorimetric determination method for heavy metal ions. This is a method of reacting an analyte with a color-developing reagent, pre-concentrating the obtained reaction product, and then performing spectroscopic analysis.
It is used in a wide range of fields.

【0003】しかしながら、この方法においては予備濃
縮が分析感度を高めるのに不可欠な工程であり、蒸発濃
縮、溶媒抽出、凝集、透析などの手段を用いて行われて
いるが、いずれも操作が煩雑である、長時間を要する、
経費がかかる、試料が不安定である、発ガン性のおそれ
のある有機溶剤を用いなければならないなどの問題があ
り、使用範囲が制限されるのを免れない。
However, in this method, preconcentration is an indispensable step for enhancing the analytical sensitivity, and it is carried out by means such as evaporative concentration, solvent extraction, coagulation, dialysis, etc., but the operation is complicated in all cases. It takes a long time,
There are problems such as high cost, unstable samples, and the need to use an organic solvent that may cause carcinogenesis, and the use range is unavoidable.

【0004】このような問題に対処するものとして、被
分析物質と特異的に反応する分子吸光係数の大きい発色
試薬[「ファインケミカル」,第20巻,第6号,第5
〜12ページ(1991)]や、被分析物質と発色試薬
との反応生成物をメンブランフィルター濃縮する方法
[「アナリスト(Analyst)」,第112巻,第
1257〜1260ページ(1987)]などが提案さ
れているが、まだ、実用に供するには、必ずしも満足し
うるものではない。
As a measure against such a problem, a coloring reagent having a large molecular extinction coefficient which reacts specifically with the substance to be analyzed ["Fine Chemical", Vol. 20, No. 6, No. 5].
~ 12 (1991)] and a method of concentrating a reaction product of an analyte and a color reagent with a membrane filter ["Analyst", Vol. 112, pp. 1257-1260 (1987)] and the like. Although proposed, it is not always satisfactory for practical use.

【0005】一方、環境分析の分野では、特に現場にお
いて試料を採取し、その試料を分析機器の完備した場所
に持ち帰って分析することが行われている。この方法は
分析精度が高いという利点はあるが、分析結果を得るま
でに長時間を要し、また経費がかさむという欠点がある
ことから、最近はその場で結果が得られるオンサイトで
の分析が望まれている。
On the other hand, in the field of environmental analysis, in particular, it is practiced to collect a sample at a site and bring the sample back to a place equipped with an analytical instrument for analysis. Although this method has the advantage of high analysis accuracy, it has the disadvantages that it takes a long time to obtain the analysis results and is expensive, so recently, on-site analysis where results can be obtained on the spot is performed. Is desired.

【0006】ところで、このオンサイトでの分析におい
ては、試料の分離及び検出に特別な装置、器具を必要と
せず、簡単な操作で、迅速かつ高感度で結果が得られ、
しかもコスト的には十分安く行いうることが要求され
る。
By the way, in this on-site analysis, no special device or instrument is required for separation and detection of the sample, and the result can be obtained quickly and with high sensitivity by simple operation.
Moreover, the cost is required to be sufficiently low.

【0007】[0007]

【発明が解決しようとする課題】本発明は、環境汚染の
原因となっている極微量成分、特に重金属イオンを簡便
かつ精度よく定量する方法、及びそれに用いる定量キッ
トを提供することを目的としてなされたものである。
SUMMARY OF THE INVENTION The present invention has been made for the purpose of providing a method for easily and accurately quantifying a trace amount of components, particularly heavy metal ions, which causes environmental pollution, and a quantification kit used therefor. It is a thing.

【0008】[0008]

【課題を解決するための手段】本発明者らは、極微量の
汚染物質を簡単に定量分析しうる方法を開発するために
鋭意研究を重ねた結果、低温において親水性、高温にお
いて疎水性となる熱可逆型感熱高分子化合物の特性を利
用することにより、簡便かつ精度よく微量汚染物質を定
量しうることを見出し、この知見に基づいて本発明をな
すに至った。
[Means for Solving the Problems] As a result of intensive studies to develop a method capable of easily quantitatively analyzing a trace amount of pollutants, the present inventors have found that it is hydrophilic at low temperatures and hydrophobic at high temperatures. By utilizing the characteristics of the thermoreversible thermosensitive polymer, it was found that a trace contaminant can be easily and accurately quantified, and the present invention has been completed based on this finding.

【0009】すなわち、本発明は、(イ)微量汚染物質
を含む環境採取試料を水と混合し、よくかきまぜたのち
静置し、その上澄液を分取し、前処理液と混合する工
程、(ロ)上記の混合液を任意温度に維持し、その温度
よりも高い転移温度をもつ低温において親水性、高温に
おいて疎水性となる微細繊維状固体の熱可逆型感熱高分
子化合物を加えて溶解させる工程、(ハ)その溶解液を
上記感熱高分子化合物の転移温度以上に昇温して固形物
を形成させたのち、この固形物から液体部分を分離する
工程、(ニ)この液体部分を、上記微量汚染物質と反応
して呈色する疎水性発色試薬を包接した固体状の低温に
おいて親水性、高温において疎水性となる熱可逆型感熱
高分子化合物と、その転移温度よりも低い温度において
混合して溶液を形成させる工程、(ホ)この溶液を転移
温度以上に昇温して、微量汚染物質と上記発色試薬との
反応によって生じた呈色化合物を包接して析出した上記
感熱高分子化合物からなる固体部分を液体部分から分離
する工程、(ヘ)(ホ)で得た固体部分を上記感熱高分
子化合物の転移温度よりも低い温度において水又は溶剤
に溶解し、溶液とする工程、及び(ト)得られた溶液の
吸光度を測定するか、或いは標準品と比色定量して微量
汚染物質の含有量を求める工程から成ることを特徴とす
る環境汚染微量物質の定量方法、及びこの方法に用いる
のに好適な、(A)必要量の前処理液を収納し、かつ試
料を加える標線を付した試験管、(B)必要量の低温に
おいて親水性、高温において疎水性となる熱可逆型感熱
高分子化合物を収納した試験管、(C)処理後(B)の
管壁に付着した親水性−疎水性熱可逆型高分子化合物固
形物から分離された液体部分を受容する試験管、(D)
定量しようとする微量汚染物質と反応して呈色する疎水
性発色試薬を包接した低温において親水性、高温におい
て疎水性となる熱可逆型高分子化合物の必要量を収納
し、かつ(C)中の液体部分を加えるための標線を付し
た試験管、(E)上記処理後に(D)の管壁に付着させ
た固形物を溶解するための溶剤を収納した小型容器、及
び(F)標準試薬により求めた微量汚染物質の濃度に対
応する比色帯を印刷した比色計を組み合わせてなる環境
汚染微量物質の定量用キットを提供するものである。
That is, according to the present invention, (a) a step of mixing an environmentally-collected sample containing trace contaminants with water, stirring them well and then leaving them to stand, and collecting the supernatant liquid and mixing with the pretreatment liquid. (B) A thermoreversible thermosensitive polymer compound of fine fibrous solid which is maintained at an arbitrary temperature of the above mixture and becomes hydrophilic at a low temperature having a transition temperature higher than that temperature and hydrophobic at a high temperature is added. A step of dissolving, (c) a step of raising the temperature of the solution above the transition temperature of the thermosensitive polymer compound to form a solid, and then separating a liquid part from the solid, (d) the liquid part A thermoreversible thermosensitive polymer compound which is hydrophilic at a low temperature and becomes hydrophobic at a high temperature in a solid state in which a hydrophobic color-forming reagent that reacts with the above-mentioned trace contaminants is included, and lower than its transition temperature. Mix at temperature to form a solution Step (e) The temperature of this solution is raised above the transition temperature, and a solid portion composed of the above heat-sensitive polymer compound is deposited by clathrating and depositing a coloring compound produced by the reaction of a trace contaminant and the above-mentioned coloring reagent. A step of separating from the liquid portion, (f) a step of dissolving the solid portion obtained in (e) in water or a solvent at a temperature lower than the transition temperature of the thermosensitive polymer compound to form a solution, and (g) Suitable for use in the method for quantifying environmental pollutants, which comprises the step of measuring the absorbance of a solution or colorimetrically determining with a standard product to determine the content of trace pollutants. , (A) a test tube containing a required amount of pretreatment liquid and having a marked line for adding a sample, (B) a thermoreversible thermosensitive polymer that is hydrophilic at a required amount of low temperature and hydrophobic at an elevated temperature A test tube containing the compound, (C After treatment deposited hydrophilic tube wall of (B) - a test tube for receiving the separated liquid portion from the hydrophobic thermally reversible polymeric compound solid, (D)
A necessary amount of a thermoreversible polymer compound, which is hydrophilic at low temperature and hydrophobic at high temperature, which contains a hydrophobic coloring reagent that develops color by reacting with a trace contaminant to be quantified, and (C) A test tube with a marked line for adding a liquid portion therein, (E) a small container containing a solvent for dissolving solid matter attached to the tube wall of (D) after the above treatment, and (F) It is intended to provide a kit for quantifying an environmental pollutant trace substance, which is a combination of a colorimeter printed with a colorimetric band corresponding to the concentration of the trace pollutant determined by a standard reagent.

【0010】[0010]

【発明の実施の形態】本発明において用いる低温におい
て親水性、高温において疎水性となる熱可逆型感熱高分
子化合物とは、所定の温度すなわち転移温度以下の低温
で生成する高分子の水和物(オキソニウムヒドロキシ
ド)が、上記温度よりも高温で脱水和することにより高
分子同士が凝集し、沈殿する物性を有するものであり、
転移温度以下では親水性を示し、水に溶解するが、転移
温度よりも高い温度では疎水性を示し、沈殿する。
BEST MODE FOR CARRYING OUT THE INVENTION A thermoreversible thermosensitive polymer compound which is hydrophilic at a low temperature and hydrophobic at a high temperature used in the present invention is a hydrate of a polymer produced at a predetermined temperature, that is, a low temperature below a transition temperature. (Oxonium hydroxide) has a physical property that macromolecules aggregate and precipitate by dehydration at a temperature higher than the above temperature,
Below the transition temperature it is hydrophilic and soluble in water, but above the transition temperature it is hydrophobic and precipitates.

【0011】本発明においては、転移温度が0〜90
℃、好ましくは10〜60℃の間にある親水性−疎水性
熱可逆型感熱高分子化合物が用いられるが、特に周囲温
度では親水性を示し、加熱すると疎水性を示すような転
移温度をもつものが好ましい。この転移温度は、高分子
化合物を構成する単量体の種類、共単量体の含有割合に
よって変えることができるが、そのほか水溶液としたと
きの塩濃度やpHを調整することによっても変えること
ができる。
In the present invention, the transition temperature is 0 to 90.
A hydrophilic-hydrophobic thermoreversible thermosensitive polymer compound having a temperature of ℃, preferably 10 to 60 ° C. is used, but it has a transition temperature that shows hydrophilicity especially at ambient temperature and shows hydrophobicity when heated. Those are preferable. This transition temperature can be changed depending on the types of monomers constituting the polymer compound and the content ratio of the comonomer, but it can also be changed by adjusting the salt concentration and pH of the aqueous solution. it can.

【0012】上記の低温において親水性、高温において
疎水性となる熱可逆型感熱高分子化合物自体は公知の物
質であり、その例としては、N‐エチルアクリルアミ
ド、N‐n‐プロピルアクリルアミド、N‐イソプロピ
ルアクリルアミド、N‐シクロプロピルアクリルアミ
ド、N,N‐エチルメチルアクリルアミド、N,N‐ジ
エチルアクリルアミド、N‐アクリロイルピロリジン、
N‐アクリロイルピペリジン、N‐アクリロイルモルホ
リン及び対応するメタクリルアミド誘導体の中から選ば
れた少なくとも1種の単量体の重合体又は共重合体、あ
るいはこれらの単量体と親水性単量体、例えばN‐ビニ
ルピロリドン、ビニルピリジン、アクリルアミド、メタ
クリルアミド、N‐メチルアクリルアミド、ヒドロキシ
エチルメタクリレート、ヒドロキシエチルアクリレー
ト、ヒドロキシメチルアクリレート、アクリル酸やメタ
クリル酸のような不飽和カルボン酸及びそれらの塩、ビ
ニルスルホン酸やスチレンスルホン酸のような不飽和ス
ルホン酸、N,N‐ジメチルアミノエチルメタクリレー
ト、N,N‐ジエチルアミノエチルメタクリレート、
N,N‐ジメチルアミノプロピルアクリルアミドなど、
あるいは疎水性単量体、例えばエチルアクリレート、メ
チルメタクリレート、グリシジルメタクリレートのよう
なアクリル酸エステル又はメタクリル酸エステルや、N
‐n‐ブチルアクリルアミド、N‐n‐ブチルメタクリ
レートのようなN‐アルキル置換アクリルアミド又はメ
タクリルアミド、塩化ビニル、アクリロニトリル、スチ
レン、酢酸ビニルなどの中から選ばれた少なくとも1種
の単量体との共重合体などが挙げられる。
The thermoreversible thermosensitive polymer compounds which are hydrophilic at low temperatures and hydrophobic at high temperatures are known substances, and examples thereof include N-ethyl acrylamide, Nn-propyl acrylamide and N-ethyl acrylamide. Isopropylacrylamide, N-cyclopropylacrylamide, N, N-ethylmethylacrylamide, N, N-diethylacrylamide, N-acryloylpyrrolidine,
Polymers or copolymers of at least one monomer selected from N-acryloylpiperidine, N-acryloylmorpholine and corresponding methacrylamide derivatives, or these monomers and hydrophilic monomers, for example N-vinylpyrrolidone, vinylpyridine, acrylamide, methacrylamide, N-methylacrylamide, hydroxyethyl methacrylate, hydroxyethyl acrylate, hydroxymethyl acrylate, unsaturated carboxylic acids such as acrylic acid and methacrylic acid, and salts thereof, vinyl sulfonic acid Unsaturated sulfonic acid such as styrene sulfonic acid, N, N-dimethylaminoethyl methacrylate, N, N-diethylaminoethyl methacrylate,
N, N-dimethylaminopropyl acrylamide, etc.
Alternatively, hydrophobic monomers such as acrylic or methacrylic acid esters such as ethyl acrylate, methyl methacrylate, glycidyl methacrylate, N
-N-butylacrylamide, N-alkyl-substituted acrylamide such as Nn-butylmethacrylate or methacrylamide, vinyl chloride, acrylonitrile, styrene, vinyl acetate and the like at least one monomer selected from Examples thereof include polymers.

【0013】一般に、親水性単量体と共重合させると単
独重合体よりも転移温度は上昇するし、また疎水性単量
体と共重合させると単独重合体よりも転移温度は低下す
るので、これを利用して所望の転移温度をもつ親水性−
疎水性熱可逆型感熱高分子化合物を形成させることがで
きる。
In general, copolymerization with a hydrophilic monomer causes a higher transition temperature than a homopolymer, and copolymerization with a hydrophobic monomer causes a lower transition temperature than a homopolymer. Utilizing this, hydrophilicity with desired transition temperature-
A hydrophobic thermoreversible thermosensitive polymer compound can be formed.

【0014】ところで、一般に環境汚染の原因となる微
量物質は、通常、土壌、排水などの巨大マトリックス中
に含有されているため、これを定量分析するには、先ず
巨大マトリックスから分析しようとする微量物質を分離
する必要がある。これまで、この分離は、微量物質を疎
水性物質、例えばキレート化合物に誘導したのち、クロ
ロホルム、エーテルなどの疎水性有機溶媒を用いて、巨
大マトリックス中から抽出することによって行われてい
たが、この方法は多量の有機溶媒を必要とする上に、抽
出効率の上からも必ずしも満足しうるものではなかっ
た。
By the way, generally, trace substances that cause environmental pollution are usually contained in a huge matrix such as soil or drainage. The substance needs to be separated. Until now, this separation was carried out by derivatizing a trace substance into a hydrophobic substance, for example, a chelate compound, and then extracting it from a huge matrix using a hydrophobic organic solvent such as chloroform or ether. The method requires a large amount of organic solvent and is not always satisfactory in terms of extraction efficiency.

【0015】しかるに、前記の熱可逆型感熱高分子化合
物を0.01〜0.5質量%の濃度で含む水溶液は、低
級アルコールに近い極性をもち、かつある濃度以上では
疎水性を示す溶媒となるものであり、しかも温度刺激に
より脱水和して固相を形成して水相と分れる性質を有し
ている。そして、疎水性マトリックスが共存すると、こ
れは熱可逆型感熱高分子化合物の固相中に取り込まれて
水相から除去され、この際の水相と固相間の分配係数
は、マトリックス物質の疎水性が高いものほど大きくな
る。
However, an aqueous solution containing the thermoreversible thermosensitive polymer compound in a concentration of 0.01 to 0.5% by mass is a solvent having a polarity close to that of a lower alcohol and having a hydrophobicity at a certain concentration or more. In addition, it has the property of being dehydrated by temperature stimulation to form a solid phase and separated from the aqueous phase. When a hydrophobic matrix coexists, it is taken into the solid phase of the thermoreversible thermosensitive polymer compound and removed from the aqueous phase. At this time, the partition coefficient between the aqueous phase and the solid phase is determined by the hydrophobicity of the matrix substance. The higher the quality, the larger.

【0016】したがって、定量しようとする微量物質を
親水性に維持し、上記の熱可逆型感熱高分子化合物をそ
の転移温度以下の温度で添加したのち、その転移温度以
上に加温すると、マトリックス物質を捕集し、分離する
ことができる。そして、この分離方法は、何らの機器も
必要とせず、単に定量すべき上澄液を傾しゃにより分取
するだけで、簡単かつ短時間で行うことができるので、
オンサイト分析における処理方法としては好適である。
Therefore, when the trace substance to be quantified is kept hydrophilic and the above thermoreversible thermosensitive polymer compound is added at a temperature below its transition temperature and then heated above that transition temperature, the matrix substance Can be collected and separated. Then, this separation method does not require any equipment, simply by collecting the supernatant to be quantified by tilting, it can be performed easily and in a short time,
It is suitable as a processing method in on-site analysis.

【0017】本発明方法においては、このような低温に
おいて親水性、高温において疎水性となる熱可逆型感熱
高分子化合物の性質を利用して、環境から採取した試料
中から定量しようとする微量汚染物質を分離する。この
微量汚染物質は、重金属イオンのような無機物質でもよ
いし、またホルムアルデヒドのような有機物質でもよ
い。
In the method of the present invention, by utilizing the property of the thermoreversible thermosensitive polymer compound which becomes hydrophilic at a low temperature and hydrophobic at a high temperature, a trace amount of contaminants to be quantified from a sample taken from the environment is used. Separate the material. The trace contaminant may be an inorganic substance such as heavy metal ions or an organic substance such as formaldehyde.

【0018】すなわち、先ず所定量の試料を環境から採
取し、水と混合して試料中の微量物質を水中へ移行さ
せ、上澄液として分取することにより、所定の基準、例
えば土壌の場合は、「土壌の汚染に係わる環境基準」
(平成3年8月23日環境庁告示第46号)に示された
調製法に従って試料液を調製する[(イ)工程]。
That is, first, a predetermined amount of a sample is taken from the environment, mixed with water to transfer a trace substance in the sample into water, and collected as a supernatant to obtain a predetermined standard, for example, in the case of soil. "Environmental standards for soil pollution"
(A step) of preparing a sample solution according to the preparation method shown in (August 23, 1991, Environmental Agency Notification No. 46).

【0019】次に、この試料液の所定量に、使用する低
温において親水性、高温において疎水性となる熱可逆型
感熱高分子化合物の転移温度よりも低い温度に保ち、こ
の微細繊維状固体の熱可逆型感熱高分子化合物を加え、
よく混合し、溶解する[(ロ)工程]。この工程におい
て混合物は単一の水相を形成している。
Next, a predetermined amount of this sample solution was kept at a temperature lower than the transition temperature of the thermoreversible thermosensitive polymer compound which becomes hydrophilic at the low temperature and hydrophobic at the high temperature, and the fine fibrous solid Add a thermoreversible thermosensitive polymer,
Mix well and dissolve [(b) step]. In this process the mixture forms a single aqueous phase.

【0020】次いで、この混合物を該熱可逆型感熱高分
子化合物の転移温度以上に昇温する。この段階で固形物
を生じ、マトリックス物質が存在する場合には、これは
固相中に取り込まれるので、傾しゃ等により液体部分の
みを固形物から分取するとマトリックス物質が除かれた
検液が得られる[(ハ)工程]。
Next, this mixture is heated to a temperature above the transition temperature of the thermoreversible thermosensitive polymer. If a solid substance is produced at this stage and a matrix substance is present, it is incorporated into the solid phase, so if only the liquid portion is separated from the solid substance by tilting or the like, a test liquid in which the matrix substance is removed is obtained. Obtained [(c) step].

【0021】次に、この検液にあらかじめ調製された微
量物質検出用材料を、その材料中に含まれる低温におい
て親水性、高温において疎水性となる熱可逆型感熱高分
子化合物の転移温度よりも低い温度において加え、溶解
させる[(ニ)工程]。
Next, the trace substance detection material prepared in advance in this test solution is more than the transition temperature of the thermoreversible thermosensitive polymer compound contained in the material, which is hydrophilic at low temperature and hydrophobic at high temperature. Add at low temperature and dissolve [step (d)].

【0022】この微量物質検出用材料は、低温において
親水性、高温において疎水性となる熱可逆型感熱高分子
化合物に疎水性キレート形成型発色試薬を包接させるこ
とによって調製される。この包接させる疎水性キレート
形成型発色試薬としては、これまで光分析において所定
の微量汚染物質とキレート化合物を形成する発色試薬と
して用いられているものの中から任意に選択して用いる
ことができる。
This trace substance detection material is prepared by including a hydrophobic chelate-forming color reagent in a thermoreversible thermosensitive polymer compound which is hydrophilic at low temperature and hydrophobic at high temperature. As the hydrophobic chelate-forming color-forming reagent to be clathrated, any one can be arbitrarily selected from those which have been used as a color-forming reagent for forming a chelate compound with a predetermined trace contaminant in photoanalysis.

【0023】このような発色試薬には、例えば、重金属
イオン検出用としてカドミウムCd(II)と赤色錯体
を形成するジチゾン、コバルトCo(II)と赤色錯体
を形成する2‐ニトロソ‐1‐ナフトール、クロムCr
(IV)と赤紫色錯体を形成するジフェニルカルバジ
ド、水銀Hg(I)及びHg(II)と黄色錯体を形成
するチオテノイルトリフルオロアセトン、鉛Pb(I
I)と赤色錯体を形成するジヂゾンなどがある。
Examples of such a coloring reagent include dithizone which forms a red complex with cadmium Cd (II) for the detection of heavy metal ions, 2-nitroso-1-naphthol which forms a red complex with cobalt Co (II), Chrome Cr
Diphenylcarbazide which forms a red-violet complex with (IV), thiothenoyltrifluoroacetone which forms a yellow complex with mercury Hg (I) and Hg (II), and lead Pb (I
I) and dizone which form a red complex.

【0024】その外、有機環境汚染物質、例えばホルム
アルデヒドの発色試薬としては、亜硫酸で脱色した色素
フクシン、N‐ベンゼンスルホニルヒドロキシルアミン
と塩化鉄との組合せ、4‐アミノ‐3‐ヒドラジノ‐5
‐メルカプト‐1,2,4‐トリアゾール、クロモトロ
ープ酸などがある。
In addition, as a color-forming reagent for organic environmental pollutants such as formaldehyde, a combination of sulfite-decolorized dye fuchsin, N-benzenesulfonylhydroxylamine and iron chloride, 4-amino-3-hydrazino-5 is used.
-Mercapto-1,2,4-triazole, chromotropic acid, etc.

【0025】本発明方法で用いる微量汚染物質検出用材
料は、前記の疎水性キレート形成型発色試薬を、水混和
性有機溶剤例えばアセトン、ジメチルホルムアミド、ジ
メチルスルホキシドなどに溶解し、得られた溶液を、前
記の親水性−疎水性熱可逆型感熱高分子化合物の水溶液
とその転移温度以下において混合し、その混合物を凍結
乾燥することによって製造することができる。
The material for detecting trace contaminants used in the method of the present invention is prepared by dissolving the above-mentioned hydrophobic chelate-forming color-developing reagent in a water-miscible organic solvent such as acetone, dimethylformamide or dimethylsulfoxide. It can be produced by mixing the above-mentioned aqueous solution of the hydrophilic-hydrophobic thermoreversible thermosensitive polymer compound at a transition temperature or lower and lyophilizing the mixture.

【0026】この際の有機溶剤中の発色試薬の濃度とし
ては、0.5〜1.0質量%の範囲内が用いられるし、
また水溶液中の感熱高分子化合物の濃度としては0.2
〜15質量%の範囲内が用いられる。凍結乾燥は、例え
ば−20℃ないし−50℃の温度において0.5〜10
0Paの減圧下で行うことができる。このようにして、
発色試薬が感熱高分子化合物中に均一に包接された綿状
の微量汚染物質検出用材料が得られる。
At this time, the concentration of the color forming reagent in the organic solvent is 0.5 to 1.0% by mass, and
The concentration of the thermosensitive polymer compound in the aqueous solution is 0.2.
Within the range of ˜15% by mass is used. Freeze-drying is, for example, 0.5-10 at a temperature of -20 ° C to -50 ° C.
It can be performed under reduced pressure of 0 Pa. In this way
A cotton-like trace contaminant detection material in which the coloring reagent is uniformly included in the thermosensitive polymer compound is obtained.

【0027】これまで、有機発色試薬は、有機溶剤に溶
解した溶液として用いられていたが、その溶液の安定性
が低く、短時間で劣化することが多かった。しかるに、
上記の微量汚染物質検出用材料は固体状であるため安定
であり、苛酷な測定条件下におけるフィールド分析にも
十分対応することができる。しかも、高分子化合物と共
存することにより、通常は水に難溶なキレート形成型発
色試薬が容易に水と混合して、速やかに呈色反応を進行
させることができる。
Up to now, the organic coloring reagent has been used as a solution dissolved in an organic solvent, but the stability of the solution is low and it often deteriorates in a short time. However,
Since the above-mentioned material for detecting trace contaminants is solid, it is stable, and can sufficiently support field analysis under severe measurement conditions. Moreover, the coexistence with the polymer compound allows the chelate-forming color-forming reagent, which is usually poorly soluble in water, to be easily mixed with water to allow the color reaction to proceed rapidly.

【0028】本発明方法においては、この微量汚染物質
検出用材料を加えた検液を、前記の感熱高分子化合物の
転移温度以上に昇温する。この処理により微量汚染物質
と発色試薬との反応によって生じた疎水性の呈色化合物
が感熱高分子化合物に包接されたまま固体状で析出し、
器壁に付着するので、固体部分をそのまま付着させて残
し、傾しゃにより液体部分のみを除く[(ホ)工程]。
In the method of the present invention, the test solution containing the trace contaminant detection material is heated to a temperature above the transition temperature of the thermosensitive polymer compound. By this treatment, the hydrophobic coloring compound produced by the reaction between the trace contaminant and the coloring reagent is deposited in a solid state while being included in the thermosensitive polymer compound,
Since it adheres to the vessel wall, the solid part is left as it is, and only the liquid part is removed by tilting [(e) step].

【0029】次に、この器壁に付着した固体部分を使用
した感熱高分子化合物の転移温度よりも低い温度の水又
は溶剤の所定量を用いて溶解し、着色溶液とする
[(ヘ)工程]。
Next, the solid portion attached to the vessel wall is dissolved using a predetermined amount of water or a solvent having a temperature lower than the transition temperature of the heat-sensitive polymer compound using the heat-sensitive polymer compound to obtain a colored solution [(f) step ].

【0030】そして、このようにして得た着色溶液につ
いて、光度計でその吸光度を測定するか、或いは標準品
と比色定量することにより、その中に含まれる微量汚染
物質の量を求める[(ト)工程]。このようにして、周
囲環境から採取した試料から、オンサイトにおいて簡
単、かつ迅速に微量汚染物質を定量することができる。
The amount of the trace contaminant contained in the colored solution thus obtained is determined by measuring its absorbance with a photometer or by colorimetrically quantifying it with a standard product [( G) process]. In this way, trace contaminants can be easily and quickly quantified on-site from a sample collected from the surrounding environment.

【0031】上記の(ト)工程の定量は、既知濃度の標
品に基づいてあらかじめ作成した標準色表と比色して行
うのが有利であるが、生成した環境汚染物質の着色溶液
の光吸収波長における吸光度を既知濃度の標品のそれと
対比して行うこともできる。
It is advantageous that the quantification in the above step (g) is performed by comparing the color with a standard color table prepared in advance based on a standard of known concentration. It is also possible to compare the absorbance at the absorption wavelength with that of a standard of known concentration.

【0032】本発明方法における低温での操作は、5〜
10℃の範囲で、また高温での操作は20〜45℃の範
囲で行うのが好ましいので、この範囲の間の転移温度を
もつ感熱高分子化合物を選んで用いるのが有利である。
The operation at low temperature in the method of the present invention is 5 to
Since it is preferable to carry out the operation in the range of 10 ° C. and the operation at high temperature in the range of 20 to 45 ° C., it is advantageous to select and use a thermosensitive polymer compound having a transition temperature in this range.

【0033】本発明方法は、各工程の操作が円滑に行い
うるように、用具を組み合わせた定量用キットを用いて
行うのが好ましい。図1は、このような定量用キットの
1例を示す斜視図である。この図に従って定量用キット
を用いて六価クロムを定量する方法を説明する。このキ
ットは、ケース1、3本の丸底試験管2,4,5と1本
の平底試験管6、溶剤を入れた小びん7、スポイト8及
び比色計9(付属品として比色帯10を含む)から構成
されている。そして、定量しようとする試料を、先ずあ
らかじめ前処理液、例えば過塩素酸混液3を収納し、試
料の必要量を示す標線を付した試験管2に、該標線の位
置まで注入し、前処理液とよく混合する。
The method of the present invention is preferably carried out using a quantification kit in which tools are combined so that the operation of each step can be carried out smoothly. FIG. 1 is a perspective view showing an example of such a quantitative kit. A method for quantifying hexavalent chromium using a quantification kit will be described with reference to this figure. This kit includes a case 1, three round-bottom test tubes 2, 4 and 5 and one flat-bottom test tube 6, a small bottle 7 containing a solvent, a dropper 8 and a colorimeter 9 (colorimetric band 10 as an accessory). Including)). Then, a sample to be quantified is first stored in advance in a pretreatment liquid, for example, perchloric acid mixed liquid 3, and injected into a test tube 2 marked with a mark indicating the required amount of the sample to the position of the marked line, Mix well with pretreatment solution.

【0034】次に、低温において親水性、高温において
疎水性となる熱可逆型感熱高分子化合物を収納した試験
管4を、該熱可逆型感熱高分子化合物の転移温度よりも
低い温度に保ち、その中へ試験管2から試料を注入す
る。次いで、この試験管4を該熱可逆型高分子化合物の
転移温度以上に加温し、激しく振り混ぜて析出した固体
を管壁に付着させ、傾しゃにより液体部分のみを試験管
5に移す。
Next, the test tube 4 containing the thermoreversible thermosensitive polymer compound which becomes hydrophilic at low temperature and hydrophobic at high temperature is kept at a temperature lower than the transition temperature of the thermoreversible thermosensitive polymer compound, A sample is injected from the test tube 2 into it. Next, the test tube 4 is heated to a temperature not lower than the transition temperature of the thermoreversible polymer compound and shaken vigorously to adhere the deposited solid to the tube wall, and only the liquid portion is transferred to the test tube 5 by tilting.

【0035】次に、疎水性発色試薬例えばジフェニルカ
ルバジドを包接した低温において親水性、高温において
疎水性となる熱可逆型高分子化合物を収納し、所要の位
置に標線を付した平底試験管6の標線の位置まで試験管
5中の液体を低温に冷却して加え、内容物を溶解させた
のち、上記熱可逆型高分子化合物の転移温度以上に加温
し、激しく振りまぜて生じた固体を管壁に付着させたの
ち、傾しゃにより液体部分を捨てて、固体部分のみを残
す。次いで、スポイト8により小びん7から少量の溶剤
を試験管6に注ぎ、固体塊を完全に溶解して着色液とす
る。
Next, a flat-bottom test was conducted in which a thermoreversible polymer compound, which included a hydrophobic color-forming reagent such as diphenylcarbazide, was hydrophilic at a low temperature and hydrophobic at a high temperature, and a marked line was drawn at a required position. After the liquid in the test tube 5 was cooled to a low temperature and added to the position of the marked line of the tube 6 to dissolve the contents, the tube was heated above the transition temperature of the thermoreversible polymer compound and shaken vigorously. After the produced solid is attached to the wall of the tube, the liquid portion is discarded by tilting, leaving only the solid portion. Next, a small amount of solvent is poured from the vial 7 into the test tube 6 with a dropper 8 to completely dissolve the solid mass to obtain a coloring liquid.

【0036】このようにして調製した着色液を収容した
平底試験管6を比色計の所定の穴に挿入し、のぞき孔を
通して比色帯の色と対比して、両者が一致するところを
求め、対応する数値を読み取ることにより、クロムの定
量を行うことができる。試験管のうち、比色計に挿入す
る試験管6は、比色帯の色と対比する場合、平底の方が
有利であるが、他の試験管は特に平底にする必要はな
い。
The flat-bottomed test tube 6 containing the coloring liquid thus prepared is inserted into a predetermined hole of the colorimeter and compared with the color of the colorimetric band through the peep hole to find the point where both match. By reading the corresponding value, the amount of chromium can be determined. Of the test tubes, the test tube 6 to be inserted into the colorimeter has a flat bottom when compared with the color of the colorimetric band, but the other test tubes do not need to have a flat bottom.

【0037】[0037]

【発明の効果】本発明方法によれば、特に所定の定量用
キットを用いることにより、簡単な操作で迅速に環境汚
染微量物質をオンサイトで定量することができる。
According to the method of the present invention, a trace amount of environmental pollutants can be rapidly quantified on-site by a simple operation, especially by using a predetermined quantification kit.

【0038】[0038]

【実施例】次に、実施例により本発明をさらに詳細に説
明するが、本発明はこれらの例によって何ら限定される
ものではない。
The present invention will be described in more detail by way of examples, which should not be construed as limiting the invention thereto.

【0039】参考例1 転移温度約30℃、質量平均分子量約50000のポリ
(N‐イソプロピルアクリルアミド)(以下PNIPA
Amと略す)4gを、ジフェニルカルパジド0.02g
をアセトン5mlに溶かした溶液中に加えて溶解し、5
℃の水を全量が100mlになるまで加えて希釈した。
次いで、この溶液を温度−40℃、圧力10Paで24
時間凍結乾操することにより、綿状のジフェニルカルパ
ジドを包接したPNIPAAm(以下DPC−PNIP
AAmと略す)を得た。
Reference Example 1 Poly (N-isopropylacrylamide) having a transition temperature of about 30 ° C. and a mass average molecular weight of about 50,000 (hereinafter referred to as PNIPA).
(Abbreviated as Am) 4 g, diphenylcarbazide 0.02 g
Was added to the solution dissolved in 5 ml of acetone and dissolved.
Diluted by adding water at ℃ until the total amount became 100 ml.
Then, this solution is placed at a temperature of -40 ° C. and a pressure of 10 Pa for 24 hours.
PNIPAAm (hereinafter DPC-PNIP) containing cotton-like diphenylcarbazide by freeze-drying for a long time
Abbreviated as AAm).

【0040】参考例2 実施例1で用いたのと同じPNIPAAm0.2gを、
ジチゾン0.001gをアセトン(orエチルアルコー
ル)5mlに溶かした溶液中に加えて溶解し、5℃の水
を全量が100mlになるまで加えて希釈した。次い
で、この溶液を参考例1と同様の条件下で凍結乾燥する
ことによりジチゾンを包接したPNIPAAm(以下D
TZ−PNIPAAmと略す)を得た。
Reference Example 2 0.2 g of the same PNIPAAm as used in Example 1,
0.001 g of dithizone was added to and dissolved in a solution of 5 ml of acetone (or ethyl alcohol), and water at 5 ° C. was added to the total amount of 100 ml for dilution. Then, this solution was freeze-dried under the same conditions as in Reference Example 1 to include dithizone-encapsulated PNIPAAm (hereinafter referred to as D
TZ-PNIPAAm) was obtained.

【0041】実施例1 クロム酸カリウム0.971gを秤取し、全量50ml
になるまで水を加えて溶解し、濃度0.1Mのクロム酸
標準原液を調製した。次いで、このクロム酸標準原液を
水で希釈してクロム含有量5.2〜156ppbのクロ
ム標準液を各10mlずつ調製した。これらのクロム標
準液10mlずつを蓋付試験管にとり、これに過塩素酸
混液(8M過塩素酸ナトリウム+0.0025M過塩素
酸)3mlを加えて混合したのち、5℃において参考例
1で得たDPC−PNIPAAmを加え振りまぜて溶解
させた。さらに、5分間この温度に保持して、Cr−D
PC錯体形成反応を完結させたのち、1分間45℃に加
温し、ただちに10秒間激しく振りまぜて、生成した固
体を試験管壁に付着させた。次いで、デカンテーション
により、液体部分を除去し、アセトン0.5mlを加え
て固体部分を溶解して赤色の溶液を得た。この溶液につ
いて波長540nmにおける吸光度を測定した結果を図
2に示す。図中の黒丸は本発明の重金属検出用材料を用
いた場合、白丸は標準液について従来の方法により測定
した場合の結果である。
Example 1 0.971 g of potassium chromate was weighed and the total amount was 50 ml.
Water was added to the solution until it became dissolved, and a chromic acid standard stock solution having a concentration of 0.1 M was prepared. Next, this chromic acid standard stock solution was diluted with water to prepare 10 ml of each chromium standard solution having a chromium content of 5.2 to 156 ppb. 10 ml of each of these chromium standard solutions was placed in a test tube with a lid, and 3 ml of a perchloric acid mixed solution (8M sodium perchlorate + 0.0025M perchloric acid) was added thereto and mixed, and then obtained at 5 ° C. in Reference Example 1. DPC-PNIPAAm was added and shaken to dissolve. Further, hold at this temperature for 5 minutes, Cr-D
After completing the PC complex formation reaction, the mixture was heated to 45 ° C. for 1 minute and immediately vigorously shaken for 10 seconds to adhere the produced solid to the test tube wall. Then, the liquid portion was removed by decantation, and 0.5 ml of acetone was added to dissolve the solid portion to obtain a red solution. The results of measuring the absorbance at a wavelength of 540 nm for this solution are shown in FIG. The black circles in the figure are the results when the heavy metal detection material of the present invention was used, and the white circles are the results when the standard solution was measured by the conventional method.

【0042】この図から分るように、Cr(VI)濃度
と吸光度とは良好な比例関係(相関係数0.999)を
示し、試料中の5ppb以上のCr(VI)は、これを
20倍以上に濃縮することにより高効率で測定すること
ができる。そして、Cr(VI)10ppb以上の試料
では目視測定が可能であるので、あらかじめ検量線の標
準溶液列の比色帯を作成しておけば、フィールドにおけ
る採取試料の測定時に、毒性の高いCr(IV)標準液
を用いることなくCr(VI)の定量を行うことができ
る。
As can be seen from this figure, the Cr (VI) concentration and the absorbance show a good proportional relationship (correlation coefficient of 0.999), and Cr (VI) of 5 ppb or more in the sample has 20% of this. By concentrating more than twice, it is possible to measure with high efficiency. Since it is possible to perform visual measurement with a sample of Cr (VI) of 10 ppb or more, if a colorimetric band of the standard solution row of the calibration curve is created in advance, highly toxic Cr ( IV) Cr (VI) can be quantified without using the standard solution.

【0043】実施例2 原子吸光用標準溶液(1000mg/l)を水で適宜に
希釈してカドミウム含有量0〜0.4mg/lの標準溶
液を調製した。これらのカドミウム標準溶液10mlず
つを蓋付試験管にとり、5℃において参考例2で得たD
TZ−PNIPAAmを加えて振り混ぜて溶解させた。
さらに10%NaOH水溶液0.1mlを加えて45℃
に10秒間加温し、直ちに10秒間激しく振り混ぜて、
生成したCd−DTZ錯体を取り込んで析出したPNI
PAAm固体を試験管壁に付着させた。次いで、デカン
テーションにより液体部分を除去し、アセトン1mlを
加えて固体部分を溶解して赤色の溶液を得た。この溶液
について波長535nmにおける吸光度を測定した結果
を図3に示す。
Example 2 A standard solution for atomic absorption (1000 mg / l) was appropriately diluted with water to prepare a standard solution having a cadmium content of 0 to 0.4 mg / l. 10 ml of each of these cadmium standard solutions was put into a test tube with a lid, and the D obtained in Reference Example 2 was obtained at 5 ° C.
TZ-PNIPAAm was added and shaken to dissolve.
Furthermore, 0.1 ml of 10% NaOH aqueous solution is added, and the temperature is 45 ° C.
Heat for 10 seconds, immediately shake vigorously for 10 seconds,
PNI deposited by incorporating the produced Cd-DTZ complex
PAAm solids were attached to the test tube wall. Then, the liquid portion was removed by decantation, and 1 ml of acetone was added to dissolve the solid portion to obtain a red solution. The result of measuring the absorbance at a wavelength of 535 nm for this solution is shown in FIG.

【0044】この図から分るように、Cd(II)濃度
と吸光度とは良好な比例関係を示し、試料液中の0.0
05mg/l以上のCd(II)は、これを20倍以上
に濃縮することにより高効率で測定できる。そして0.
01mg/l以上の試料では目視測定が可能である。従
って、予め標準溶液列の比色表を作製しておけばフィー
ルドにおける測定時に、毒性の高いCd(II)標準液
を用いることなくCd(II)の定量を行うことができ
る。
As can be seen from this figure, the Cd (II) concentration and the absorbance show a good proportional relationship, with 0.0
Cd (II) of 05 mg / l or more can be measured with high efficiency by concentrating it 20 times or more. And 0.
Visual measurement is possible with a sample of 01 mg / l or more. Therefore, if a colorimetric table of a standard solution row is prepared in advance, it is possible to quantify Cd (II) at the time of measurement in the field without using a highly toxic Cd (II) standard solution.

【図面の簡単な説明】[Brief description of drawings]

【図1】 本発明キットの斜視図。FIG. 1 is a perspective view of a kit of the present invention.

【図2】 Cr(VI)の濃度と波長540nmにおけ
る吸光度との関係を示すグラフ。
FIG. 2 is a graph showing the relationship between the concentration of Cr (VI) and the absorbance at a wavelength of 540 nm.

【図3】 Cd(II)の濃度と波長535nmにおけ
る吸光度との関係を示すグラフ。
FIG. 3 is a graph showing the relationship between the concentration of Cd (II) and the absorbance at a wavelength of 535 nm.

【符号の説明】[Explanation of symbols]

1 ケース 2,4,5,6 試験管 3 前処理液 7 小びん 8 スポイト 9 比色計 10 比色帯 1 case 2, 4, 5, 6 test tube 3 Pretreatment liquid 7 small bottles 8 dropper 9 Colorimeter 10 Colorimetric band

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 2G042 BC11 DA06 DA08 2G054 AB07 CA10 CE01 EA06    ─────────────────────────────────────────────────── ─── Continued front page    F-term (reference) 2G042 BC11 DA06 DA08                 2G054 AB07 CA10 CE01 EA06

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 (イ)微量汚染物質を含む環境採取試料
を水と混合し、よくかきまぜたのち静置し、その上澄液
を分取し、前処理液と混合する工程、(ロ)上記の混合
液を任意温度に維持し、その温度よりも高い転移温度を
もつ低温において親水性、高温において疎水性となる微
細繊維状固体の熱可逆型感熱高分子化合物を加えて溶解
させる工程、(ハ)その溶解液を上記感熱高分子化合物
の転移温度以上に昇温して固形物を形成させたのち、こ
の固形物から液体部分を分離する工程、(ニ)この液体
部分を、上記微量汚染物質と反応して呈色する疎水性発
色試薬を包接した固体状の低温において親水性、高温に
おいて疎水性となる熱可逆型感熱高分子化合物と、その
転移温度よりも低い温度において混合して溶液を形成さ
せる工程、(ホ)この溶液を転移温度以上に昇温して、
微量汚染物質と上記発色試薬との反応によって生じた呈
色化合物を包接して析出した上記感熱高分子化合物から
なる固体部分を液体部分から分離する工程、(ヘ)
(ホ)で得た固体部分を上記感熱高分子化合物の転移温
度よりも低い温度において水又は溶剤に溶解し、溶液と
する工程、及び(ト)得られた溶液の吸光度を測定する
か、或いは標準品と比色定量して微量汚染物質の含有量
を求める工程から成ることを特徴とする環境汚染微量物
質の定量方法。
1. A step of: (a) mixing an environmentally-collected sample containing trace contaminants with water, stirring well, allowing to stand, collecting the supernatant, and mixing with a pretreatment liquid; (b) A step of maintaining the above-mentioned mixed liquid at an arbitrary temperature, adding a thermoreversible thermosensitive polymer compound of a fine fibrous solid which becomes hydrophilic at a low temperature having a transition temperature higher than that temperature and becomes hydrophobic at a high temperature, (C) A step of raising the temperature of the solution above the transition temperature of the thermosensitive polymer compound to form a solid, and then separating a liquid portion from the solid; A thermoreversible thermosensitive polymer compound that is hydrophilic at low temperatures and hydrophobic at high temperatures is mixed with a thermoreversible thermosensitive polymer compound in the form of a solid that encloses a hydrophobic coloring reagent that reacts with contaminants and is mixed at a temperature lower than its transition temperature. To form a solution, (e) The temperature of the solution above is raised above the transition temperature,
A step of separating from a liquid portion a solid portion composed of the above thermosensitive polymer compound deposited by inclusion of a coloring compound generated by the reaction of a trace contaminant and the above coloring reagent;
(E) Dissolving the solid part obtained in (b) in water or a solvent at a temperature lower than the transition temperature of the thermosensitive polymer compound to form a solution, and (g) measuring the absorbance of the obtained solution, or A method for quantifying a trace amount of environmental pollutants, which comprises the step of determining the content of a trace pollutant by colorimetrically quantifying a standard product.
【請求項2】 (イ)工程における微量汚染物質が重金
属である請求項1記載の環境汚染微量物質の定量方法。
2. The method for quantifying environmental pollutant according to claim 1, wherein the trace pollutant in the step (a) is a heavy metal.
【請求項3】 (イ)工程における微量汚染物質が有害
無機又は有機物質である請求項1記載の環境汚染微量物
質の定量方法。
3. The method for quantifying trace environmental pollutants according to claim 1, wherein the trace pollutants in the step (a) are harmful inorganic or organic substances.
【請求項4】 (ニ)工程における微量汚染物質と反応
して呈色する疎水性発色試薬が、重金属イオンとキレー
ト化合物を形成して呈色する疎水性キレート形成型試薬
である請求項2記載の環境汚染微量物質の定量方法。
4. A hydrophobic chelate-forming reagent, which is colored by reacting with a trace contaminant in step (d), is a hydrophobic chelate-forming reagent which forms a chelate compound with a heavy metal ion and is colored. Method for quantifying trace substances of environmental pollution.
【請求項5】 (A)必要量の前処理液を収納し、かつ
試料を加える標線を付した試験管、(B)必要量の低温
において親水性、高温において疎水性となる熱可逆型感
熱高分子化合物を収納した試験管、(C)処理後(B)
の管壁に付着した親水性−疎水性熱可逆型高分子化合物
固形物から分離された液体部分を受容する試験管、
(D)定量しようとする微量汚染物質と反応して呈色す
る疎水性発色試薬を包接した低温において親水性、高温
において疎水性となる熱可逆型高分子化合物の必要量を
収納し、かつ(C)中の液体部分を加えるための標線を
付した試験管、(E)上記処理後に(D)の管壁に付着
させた固形物を溶解するための溶剤を収納した小型容
器、及び(F)標準試薬により求めた微量汚染物質の濃
度に対応する比色帯を印刷した比色計を組み合わせてな
る環境汚染微量物質の定量用キット。
5. A thermoreversible type (A) a test tube containing a required amount of pretreatment liquid and having a marked line for adding a sample, and (B) a hydrophilic amount at a required amount of low temperature and hydrophobic at an elevated temperature. Test tube containing thermosensitive polymer, (C) after treatment (B)
A test tube for receiving a liquid portion separated from a hydrophilic-hydrophobic thermoreversible polymer compound solid adhered to the tube wall of
(D) A necessary amount of a thermoreversible polymer compound which is hydrophilic at a low temperature and which is hydrophobic at a high temperature, which contains a hydrophobic coloring reagent which is colored by reacting with a trace contaminant to be quantified, and (C) a test tube with a marked line for adding a liquid portion in (C), (E) a small container containing a solvent for dissolving solid matter adhered to the tube wall of (D) after the above treatment, and (F) A kit for quantifying environmental pollutant trace substances, comprising a colorimeter printed with a colorimetric band corresponding to the concentration of trace pollutants determined by a standard reagent.
【請求項6】 (B)の低温において親水性、高温にお
いて疎水性となる熱可逆型感熱高分子化合物が、ポリ
(N‐イソプロピルアクリルアミド)であり、(D)の
定量しようとする微量汚染物質がクロム、それと反応し
て呈色する疎水性発色試薬を包接した低温において親水
性、高温において疎水性となる熱可逆型高分子化合物
が、ジフェニルカルバジドを包接したポリ(N‐イソプ
ロピルアクリルアミド)であり、(E)の溶剤がアセト
ンである請求項5記載の定量用キット。
6. The thermoreversible thermosensitive polymer compound which is hydrophilic at low temperature and hydrophobic at high temperature in (B) is poly (N-isopropylacrylamide), and (D) is a trace contaminant to be quantified. Is a chromium, and a thermoreversible polymer compound that is hydrophilic at low temperature and is hydrophobic at high temperature in which a hydrophobic color-forming reagent that reacts with it is included in poly (N-isopropylacrylamide) ), And the solvent of (E) is acetone.
【請求項7】 (B)の低温において親水性、高温にお
いて疎水性となる熱可逆型感熱高分子化合物がポリ(N
‐イソプロピルアクリルアミド)であり、(D)定量し
ようとする微量環境汚染物質がカドミウム、それと反応
して呈色する疎水性発色試薬を包接した低温において親
水性、高温において疎水性となる熱可逆型高分子化合物
が、ジチゾンを包接したポリ(N‐イソプロピルアクリ
ルアミド)であり、(E)の溶剤がアセトンである請求
項5記載の定量用キット。
7. The thermoreversible thermosensitive polymer compound (B), which is hydrophilic at low temperature and hydrophobic at high temperature, is poly (N).
-Isopropylacrylamide), and (D) a trace amount of environmental pollutant to be quantified is cadmium, which is a thermoreversible type that becomes hydrophilic at low temperature and becomes hydrophobic at high temperature by including a hydrophobic coloring reagent that develops color by reacting with it. The quantitative kit according to claim 5, wherein the polymer compound is poly (N-isopropylacrylamide) including dithizone, and the solvent of (E) is acetone.
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