KR100461702B1 - Determination Method of Glyphosate, Endothall and Chloramben in Water Samples - Google Patents
Determination Method of Glyphosate, Endothall and Chloramben in Water Samples Download PDFInfo
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- KR100461702B1 KR100461702B1 KR10-2002-0016909A KR20020016909A KR100461702B1 KR 100461702 B1 KR100461702 B1 KR 100461702B1 KR 20020016909 A KR20020016909 A KR 20020016909A KR 100461702 B1 KR100461702 B1 KR 100461702B1
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 21
- 238000000034 method Methods 0.000 title claims abstract description 14
- 239000005562 Glyphosate Substances 0.000 title claims abstract description 7
- XDDAORKBJWWYJS-UHFFFAOYSA-N glyphosate Chemical compound OC(=O)CNCP(O)(O)=O XDDAORKBJWWYJS-UHFFFAOYSA-N 0.000 title claims abstract description 7
- 229940097068 glyphosate Drugs 0.000 title claims abstract description 7
- HSSBORCLYSCBJR-UHFFFAOYSA-N Chloramben Chemical compound NC1=CC(Cl)=CC(C(O)=O)=C1Cl HSSBORCLYSCBJR-UHFFFAOYSA-N 0.000 title claims abstract description 5
- GXEKYRXVRROBEV-FBXFSONDSA-N (1r,2s,3r,4s)-7-oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid Chemical compound C1C[C@@H]2[C@@H](C(O)=O)[C@@H](C(=O)O)[C@H]1O2 GXEKYRXVRROBEV-FBXFSONDSA-N 0.000 title description 2
- 239000004009 herbicide Substances 0.000 claims abstract description 27
- 238000004817 gas chromatography Methods 0.000 claims abstract description 23
- 238000004458 analytical method Methods 0.000 claims abstract description 22
- RHQDFWAXVIIEBN-UHFFFAOYSA-N Trifluoroethanol Chemical compound OCC(F)(F)F RHQDFWAXVIIEBN-UHFFFAOYSA-N 0.000 claims abstract description 15
- QAEDZJGFFMLHHQ-UHFFFAOYSA-N trifluoroacetic anhydride Chemical compound FC(F)(F)C(=O)OC(=O)C(F)(F)F QAEDZJGFFMLHHQ-UHFFFAOYSA-N 0.000 claims description 18
- 238000001212 derivatisation Methods 0.000 claims description 7
- 239000003960 organic solvent Substances 0.000 claims description 4
- 238000011088 calibration curve Methods 0.000 claims description 3
- 150000008064 anhydrides Chemical class 0.000 claims description 2
- 230000007613 environmental effect Effects 0.000 claims description 2
- 238000007738 vacuum evaporation Methods 0.000 claims 1
- 238000000605 extraction Methods 0.000 abstract description 12
- 238000006243 chemical reaction Methods 0.000 abstract description 11
- 239000000575 pesticide Substances 0.000 abstract description 10
- 239000002904 solvent Substances 0.000 abstract description 7
- 230000035945 sensitivity Effects 0.000 abstract description 6
- 230000002378 acidificating effect Effects 0.000 abstract description 4
- 239000003651 drinking water Substances 0.000 abstract description 4
- 235000020188 drinking water Nutrition 0.000 abstract description 4
- 238000004904 shortening Methods 0.000 abstract description 3
- 238000004949 mass spectrometry Methods 0.000 abstract description 2
- 238000011109 contamination Methods 0.000 abstract 1
- 230000002265 prevention Effects 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- XEKOWRVHYACXOJ-UHFFFAOYSA-N Ethyl acetate Chemical compound CCOC(C)=O XEKOWRVHYACXOJ-UHFFFAOYSA-N 0.000 description 6
- 239000007789 gas Substances 0.000 description 6
- 238000002290 gas chromatography-mass spectrometry Methods 0.000 description 5
- 238000001514 detection method Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 230000035484 reaction time Effects 0.000 description 4
- GXMWLJKTGBZMBH-UHFFFAOYSA-N 2-(2,4-dichlorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=C(Cl)C=C1Cl GXMWLJKTGBZMBH-UHFFFAOYSA-N 0.000 description 3
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- YMWUJEATGCHHMB-UHFFFAOYSA-N Dichloromethane Chemical compound ClCCl YMWUJEATGCHHMB-UHFFFAOYSA-N 0.000 description 3
- 239000002253 acid Substances 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 description 2
- YXHKONLOYHBTNS-UHFFFAOYSA-N Diazomethane Chemical compound C=[N+]=[N-] YXHKONLOYHBTNS-UHFFFAOYSA-N 0.000 description 2
- RTZKZFJDLAIYFH-UHFFFAOYSA-N Diethyl ether Chemical compound CCOCC RTZKZFJDLAIYFH-UHFFFAOYSA-N 0.000 description 2
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 239000001307 helium Substances 0.000 description 2
- 229910052734 helium Inorganic materials 0.000 description 2
- SWQJXJOGLNCZEY-UHFFFAOYSA-N helium atom Chemical compound [He] SWQJXJOGLNCZEY-UHFFFAOYSA-N 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 238000001819 mass spectrum Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 238000011002 quantification Methods 0.000 description 2
- 238000002098 selective ion monitoring Methods 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- 125000003277 amino group Chemical group 0.000 description 1
- 238000004587 chromatography analysis Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- HVTICUPFWKNHNG-UHFFFAOYSA-N iodoethane Chemical compound CCI HVTICUPFWKNHNG-UHFFFAOYSA-N 0.000 description 1
- INQOMBQAUSQDDS-UHFFFAOYSA-N iodomethane Chemical compound IC INQOMBQAUSQDDS-UHFFFAOYSA-N 0.000 description 1
- 238000000752 ionisation method Methods 0.000 description 1
- 238000004811 liquid chromatography Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- PVWOIHVRPOBWPI-UHFFFAOYSA-N n-propyl iodide Chemical compound CCCI PVWOIHVRPOBWPI-UHFFFAOYSA-N 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000009938 salting Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000004454 trace mineral analysis Methods 0.000 description 1
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- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/18—Water
- G01N33/1826—Organic contamination in water
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- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N1/00—Sampling; Preparing specimens for investigation
- G01N1/28—Preparing specimens for investigation including physical details of (bio-)chemical methods covered elsewhere, e.g. G01N33/50, C12Q
- G01N1/40—Concentrating samples
- G01N1/4022—Concentrating samples by thermal techniques; Phase changes
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- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
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- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
- G01N30/04—Preparation or injection of sample to be analysed
- G01N30/06—Preparation
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- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
- G01N30/62—Detectors specially adapted therefor
- G01N30/72—Mass spectrometers
- G01N30/7206—Mass spectrometers interfaced to gas chromatograph
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- G01N33/184—Herbicides, pesticides, fungicides, insecticides or the like
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- G01N1/40—Concentrating samples
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Abstract
본 발명은 음용수 및 수질 시료에 함유된 글리포세이트, 엔도탈 및 클로람벤 등 3종의 제초제를 동시 분석하기 위하여, 농축하는 방법을 사용하였으며, 농축후 트리플루오로무수아세트산과 트리플루오로에탄올을 반응시켜 3종 산성 농약을 유도체화한 후 그 농도를 결정하는 것을 특징으로 한다. 상기 방법은 기체 크로마토그래피 (GC) 또는 기체 크로마토그래피 (GC)-질량 분석기 (MS)를 사용하여 위의 3종 제초제의 농도를 분석하는 것으로 이루어진다. 본 발명의 방법에 의해 수질 시료 중에서 분석할 경우, 우수한 감도, 분석 시간의 단축 및 간편성, 경제성, 추출용매 사용시 발생되는 2차 오염의 예방 등을 동시에 얻을 수 있다.In the present invention, in order to simultaneously analyze three herbicides such as glyphosate, endortal and chlorambene contained in drinking water and water samples, the concentration method was used. After concentration, trifluoroanhydride and trifluoroethanol were concentrated. After the reaction, the three acidic pesticides are derivatized and their concentrations are determined. The method consists in analyzing the concentrations of the three herbicides above using gas chromatography (GC) or gas chromatography (GC) -mass spectrometry (MS). When analyzing in a water sample by the method of the present invention, it is possible to simultaneously obtain excellent sensitivity, shortening and simplicity of analysis time, economy, and prevention of secondary contamination generated when using an extraction solvent.
Description
본 발명은 음용수 및 수질시료에서 글리포세이트(glyphosate), 엔도탈 (endothall), 클로람벤 (chloramben) 등의 3종 산성농약을 동시에 검출하는 검출법으로, 더욱 상세하게 위의 3종 농약을 진공회전증발기를 이용하여 농축한 후, 일정한 반응 시간 및 온도 하에서 트리플루오로무수아세트산과 트리플루오로에탄올 (trifluoroethanol)을 반응시켜 3종의 농약을 유도체화 한 후, 이를 직접 기체 크로마토그래피(GC) 또는 기체 크로마토그래피/질량분석기(GC/MS)를 사용하여 분석함으로써 산성농약을하는 방법에 관한 것이다. 본 발명의 방법은 우수한 감도, 분석시간의 단축 및 간편성, 경제성 등의 장점을 갖추고 있어서, 수질에서 미량으로 잔류하는 농약의 모니터링에 효과적으로 널리 응용될 수 있다.The present invention is a detection method for simultaneously detecting three acidic pesticides such as glyphosate, endothall, and chloramben in drinking water and water samples, and vacuum rotating the above three pesticides in more detail. After concentration using an evaporator, trifluoroethanol was reacted with trifluoroacetic anhydride and trifluoroethanol under a constant reaction time and temperature, and then three kinds of pesticides were derivatized, and then directly subjected to gas chromatography (GC) or gas. It relates to a method for acidic pesticides by analyzing using chromatography / mass spectrometry (GC / MS). The method of the present invention has advantages such as excellent sensitivity, shortening and simplicity of analysis time, and economic efficiency, and thus can be effectively applied to monitoring pesticides remaining in trace amounts in water quality.
분석하고자 하는 3가지의 농약은 제초제로 많이 쓰이고 있으며 값이 비교적 싸고 적은 양으로도 효과를 볼 수 있기 때문에 세계적으로 폭 넓게 사용되어 왔다 [Analytica Chimica Acta 414, 79-84 (2000)]. 그러나 이러한 유해물질의 남용으로 인하여 사용 후에 강이나 호수, 지하수, 토양 등으로 스며들어 환경을 오염시키고 있다고 보고되고 있다 [J. Agric. Food. Chem., 38, 142 (1990)].The three pesticides to be analyzed are widely used as herbicides and have been widely used worldwide because they are relatively inexpensive and can be effective in small amounts (Analytica Chimica Acta 414, 79-84 (2000)). However, it has been reported that after the use of these harmful substances seep into the river, lake, groundwater, soil, etc. after use, it pollutes the environment [J. Agric. Food. Chem., 38, 142 (1990)].
본 발명에서 분석한 물질은 모두 3 종으로 글리포세이트, 엔도탈, 클로람벤 등이다. 이러한 농약들은 이제까지 동시에 분석된 경우는 없었다. 또한 이 중 글리포세이트는 일반적인 유기 용매에는 거의 녹지 않으며, 물에 대한 용해도는 0.012g/㎖ 정도이다. 이러한 이유로 추출이 매우 어려운 물질이었다. 상기 3가지 물질은 분자 내에 카르복시기(-COOH)와 아미노기(-NH) 등을 가지고 있어서 극성이 큰 편으로 이것을 자체로 분석하는 경우에 미량 분석에 문제가 있거나, 가스 크로마토그래피로는 검출이 불가능한 경우가 있다. 이러한 이유로 인하여 이들 농약을 분석하기 위하여 주로 액채크로마토그래피를 이용하여 분석하거나, 다이아조메탄 (diazomethane) 또는 PFPH를 이용하여 유도체화 검출하는 방법이 사용되어 왔다. 그러나, 이들 시약은 사용이 위험하거나 독성이 심한 단점 등 여러 가지 문제점이 지적되었다. 따라서, 신속하고 경제적이며 미량까지 분석이 가능한 안정적인 검출법이 요구되어 왔다.All three substances analyzed in the present invention are glyphosate, endortal and chlorambene. These pesticides have never been analyzed simultaneously. In addition, glyphosate is hardly soluble in a general organic solvent, solubility in water is about 0.012g / ㎖. For this reason, extraction was very difficult. The three substances have a carboxyl group (-COOH) and an amino group (-NH) in the molecule, and thus have a high polarity, and thus have problems in trace analysis when they are analyzed by themselves, or when gas chromatography cannot detect them. There is. For this reason, in order to analyze these pesticides, a method mainly using liquid chromatography or analyzing using diazomethane or diazomethane or PFPH has been used. However, a number of problems have been pointed out, such as disadvantages that these reagents are dangerous to use or are highly toxic. Therefore, there has been a demand for a stable detection method that can be analyzed quickly, economically and in trace amounts.
따라서, 본 발명은 동시 추출이 어려운 3종의 제초제를 수질시료 중에서 효과적으로 분석할 수 있도록 하며, 기체 크로마토그래피 또는 기체크로마토그래피/질량분석기에 대해서 선택적이고 우수한 감도를 갖는 분석 방법을 제공함으로써 우수한 감도, 재현성 향상, 정확성, 분석시간의 단축, 저비용 및 간편성 등을 만족시킬 수 있으며, 이로 인해 인체에 유해한 물질인 3종의 제초제를 수질시료에서 동시에 정량적으로 분석할 수 있어 환경시료 특히 수질시료 분석에 폭 넓게 응용할 수 있는 분석 방법을 제공하는 것을 목적으로 한다.Accordingly, the present invention enables effective analysis of three herbicides, which are difficult to co-extract, in a water sample, and provides an analytical method having selective and excellent sensitivity to gas chromatography or gas chromatography / mass spectrometer. Improved reproducibility, accuracy, shortened analysis time, low cost and simplicity can be satisfied. As a result, three herbicides, which are harmful to humans, can be analyzed quantitatively at the same time in water samples. The aim is to provide a widely applicable analytical method.
도 1은 본 발명에서 추출용매 및 농축에 따른 추출회수율을 나타낸 것이다.Figure 1 shows the extraction recovery rate according to the extraction solvent and concentration in the present invention.
도 2는 본 발명에서 3종 제초제를 기체크로마토그래피/질량분석기로 분석한 크로마토그램을 나타낸 것이다.Figure 2 shows the chromatogram of the three herbicides analyzed by gas chromatography / mass spectrometry in the present invention.
도 3은 본 발명에서 유도체화된 3종 제초제의 질량스펙트럼을 나타낸 것이다.Figure 3 shows the mass spectrum of the three herbicides derivatized in the present invention.
도 4는 본 발명에서 정량을 위한 검량곡선을 나타낸 것이다.Figure 4 shows the calibration curve for quantification in the present invention.
본 발명자들은 음용수 및 수질시료에서 추출이 어려운 3종의 제초제를 효과적으로 분석하기 위하여, 물시료를 직접 증발, 농축시키는 방법을 이용하였다. 농축 후에 이 세 가지 물질을 트리플루오로무수아세트산과 트리플루오로에탄올로 반응시켜 유도체화 한 결과, 이를 직접 기체 크로마토그래피 또는 기체 크로마토그래피/질량 분석기를 사용하여 3 종 제초제의 미량 농도를 분석하는 동시 검출법이 가능하게 되었다.The present inventors used a method of directly evaporating and concentrating a water sample to effectively analyze three herbicides that are difficult to extract from drinking water and water samples. After concentration, these three materials were derivatized by reacting with trifluoroacetic anhydride and trifluoroethanol, which were then analyzed by direct gas chromatography or gas chromatography / mass spectrometry to analyze trace concentrations of the three herbicides. The detection method became possible.
이와 같은 본 발명을 상세하게 설명하면 다음과 같다.The present invention will be described in detail as follows.
본 발명에서는 음용수 및 수질 시료로부터 3종 제초제를 분석하기 위하여 농축하는 방법을 채용한다. 이들 물질은 유기용매에 대한 추출율이 매우 낮기 때문에 용매로 추출하는 데에는 어려움이 있다. 또한 이들 3종의 물질은 현재까지 동시 추출 및 분석에 관한 실험보고가 없었다. 본 발명에서는 이러한 단점을 보완하기 위하여 유기용매를 사용하여 추출하지 않고 5 내지 10 ㎖의 물을 직접 진공회전 증발기를 이용하여 완전히 건조시킨 후 트리플루오로무수아세트산과 트리플루오로에탄올로 반응시켜 3종 제초제를 모두 유도체화한다. 이러한 유도체화 반응은 다음 반응식 1과 같다.In the present invention, a method of concentrating to analyze three herbicides from drinking water and water samples is employed. These materials are difficult to extract with a solvent because the extraction rate with respect to the organic solvent is very low. In addition, there are no experimental reports on simultaneous extraction and analysis of these three materials. In the present invention, in order to compensate for this disadvantage, 5-10 ml of water is completely dried using a direct vacuum rotary evaporator without using an organic solvent and then reacted with trifluoroacetic anhydride and trifluoroethanol. All herbicides are derivatized. This derivatization reaction is shown in Scheme 1 below.
상기 반응식 1의 유도체화 과정에서 3종 농약의 트리플루오로무수아세트산 및 트리플루오로에탄올과의 반응시간이 특히 중요하다. 트리플루오로무수아세트산의 양은 50 내지 150 ㎕, 바람직하게는 100 ㎕가 적당하며, 트리플루오로에탄올의 양은 25 내지 100 ㎕, 바람직하게는 50 ㎕가 적당하며, 반응온도는 60 내지 90 ℃,바람직하게는 80 ℃가 적당하며, 반응시간은 30 내지 120분, 바람직하게는 60분으로 한다. 이러한 조건으로 상기 유도체화 반응을 수행하면 상기 반응식 1에 표시되어 있는 화합물을 얻을 수 있다. 상기 방법은 3종 제초제를 유도체화시키는 최적의 조건이 되며, 기체 크로마토그래피 또는 기체크로마토그래피/질량 분석기에 감도 및 선택성이 좋고 보다 향상된 검출한계를 제공한다.In the derivatization process of Scheme 1, the reaction time with trifluoroacetic anhydride and trifluoroethanol of three pesticides is particularly important. The amount of trifluoro anhydrous acetic acid is 50 to 150 μl, preferably 100 μl is suitable, the amount of trifluoroethanol is 25 to 100 μl, preferably 50 μl, and the reaction temperature is 60 to 90 ℃, preferably Preferably 80 ° C is suitable, and the reaction time is 30 to 120 minutes, preferably 60 minutes. When the derivatization reaction is performed under these conditions, the compound represented by Scheme 1 can be obtained. The method is an optimal condition for derivatization of the three herbicides, and provides gas chromatography or gas chromatography / mass spectrometers with better sensitivity and selectivity and better detection limits.
유도체화된 3종 산성제초제의 분석은 기체 크로마토그래피 또는 기체크로마토그래피/질량분석기를 사용하여 수행하게 되며, 구체적으로는 기체 크로마토그래피에 주입시키고, 산화에 불활성인 기체를 이동상으로 사용하여 행한다. 이동상으로 사용될 수 있는 기체는 기체 크로마토그래피에 사용되는 통상의 기체면 어느것이나 사용가능하다. 바람직하게는 산화에 불활성인 질소, 헬륨 및 수소 등을 사용할 수 있다. 컬럼의 길이와 내경 등은 중간 정도 극성을 가진 컬럼이면 사용가능하다.Analysis of the derivatized three acid herbicides is carried out using gas chromatography or gas chromatography / mass spectrometry, specifically injected into gas chromatography and using a gas inert to oxidation as the mobile phase. Gas that can be used as the mobile phase can be any conventional gas used in gas chromatography. Preferably, nitrogen, helium, hydrogen or the like which is inert to oxidation can be used. The length and inner diameter of the column can be used as long as the column has a medium polarity.
이하, 본 발명을 다음 실시예에 의거하여 더욱 상세하게 설명하겠는 바, 본 발명이 다음 실시예에 한정되는 것은 아니다.Hereinafter, the present invention will be described in more detail based on the following examples, but the present invention is not limited to the following examples.
실시예Example
실시예 1Example 1
공시험관을 4개 준비하여 각각의 시험관에 3종 제초제의 표준물질 10 ㎍/㎖용액을 각각 50 ㎕씩 넣고, 내부표준 물질인 2,4-디클로로페닐아세트산용액 10 ㎍/㎖를 10 ㎕씩 모두 첨가한 후, 여기에 4개의 시험관 중 3개의 시험관에 각각 요오드화메틸, 요오드화에틸, 요오드화프로필을 50 ㎕씩 첨가한 후, 아세톤 150 ㎕를넣어주고 여기에 탄산칼륨 분말을 약 2 내지 3 mg 정도 첨가하였다. 나머지 다른 하나의 시험관에는 트리플루오로무수아세트산과 트리플루오로에탄올을 첨가하여 각각을 80 ℃에서 1시간 반응시켰다. 그 결과 위의 4가지 반응 중 3가지는 반응이 일어나지 않았으며, 트리플루오로무수아세트산과 트리플루오로에탄올로 반응시킨 것만 반응이 일어났다.Four blank test tubes were prepared, and 50 μl of 10 μg / ml solution of the three kinds of herbicides were added to each test tube, and 10 μl of 10 μg / ml of 2,4-dichlorophenylacetic acid solution, which is an internal standard. After the addition, 50 μl of methyl iodide, ethyl iodide, and propyl iodide were added to three test tubes of four test tubes, and then 150 μl of acetone was added thereto, and about 2 to 3 mg of potassium carbonate powder was added thereto. It was. In another test tube, trifluoroacetic anhydride and trifluoroethanol were added, and each was reacted at 80 ° C for 1 hour. As a result, three of the above four reactions did not occur, only the reaction with trifluoroacetic anhydride and trifluoroethanol occurred.
실시예 2Example 2
3개의 25 ㎖의 분액 깔대기에 각각 10 ㎖의 증류수를 넣고 3종 제초제의 표준물질 10㎍/㎖ 용액을 각각 50㎕씩 넣고, 내부표준 물질인 2,4-디클로로페닐아세트산용액 10㎍/㎖를 10㎕씩 모두 첨가한다. 2개의 시료에는 염석 효과를 꾀하기 위하여 2g 정도의 무수황산나트륨을 넣어준 후, 2개 중 1개의 분액깔대기에는 에틸에테르를 나머지 다른 분액깔대기에는 메틸렌클로라이드를 5 ㎖씩 각각 가하고 15분간 진탕한 후 추출한다. 추출 후의 물층을 제거한 다음, 추출용매를 완전히 날린다. 추출하여 나온 용매층의 물기를 제거하고 2개의 시료 모두 농축 후 남은 잔사에 각각 트리플루오로무수아세트산 100 ㎕와 트리플루오로에탄올 50 ㎕을 첨가하여 유도체화 과정으로 들어갔다. 추출과정을 거치지 않은 나머지 1개의 시료는 직접 회전진공증발기를 사용하여 수분을 완전히 제거한 후 트리플루오로무수아세트산 100 ㎕와 트리플루오로에탄올 50 ㎕을 첨가하여 유도체화 과정으로 들어갔다. 80 ℃에서 1시간 동안 가열한 후 반응을 완성시키고 냉각시킨 다음, 다시 질소 하에서 건조시키고 시료를 에틸아세테이트용액 100 ㎕로 다시 용해시킨 후 직접 기체 크로마토그래피에 2 ㎕ 주입하여 분석하였다. 본 실시예에서는 추출용매에 따른 추출율을 보기 위한 것이다. 그 결과는 도 1에 나타낸 것과 같고 용매를 사용하여 추출한 결과 거의 추출이 되지 않았으며, 진공회전증발기를 이용하여 시료를 직접 농축한 것만이 좋은 결과를 나타냈다.10 ml of distilled water was put into three 25 ml separating funnels, and 50 µl of 10 µg / ml solutions of three kinds of herbicides were added, and 10 µg / ml of 2,4-dichlorophenylacetic acid solution, an internal standard, was added. Add 10 μl each. 2 g of anhydrous sodium sulfate is added to the two samples for salting effect, 1 part of two funnels are ethyl ether and 5 ml of methylene chloride is added to the other funnel and shaken for 15 minutes. . After removing the water layer after extraction, the extraction solvent is blown off completely. Water was removed from the solvent layer and the two samples were concentrated and 100 µl of trifluoroacetic anhydride and 50 µl of trifluoroethanol were added to the remaining residue, respectively, to enter the derivatization process. One sample that was not subjected to the extraction process was completely dehydrated using a direct rotary vacuum evaporator, followed by derivatization by adding 100 μl of trifluoroacetic anhydride and 50 μl of trifluoroethanol. After heating at 80 ° C. for 1 hour, the reaction was completed, cooled, dried under nitrogen again, the sample was dissolved in 100 μl of ethyl acetate solution, and injected directly into 2 μl of gas chromatography for analysis. In this embodiment, the extraction rate according to the extraction solvent is intended. The results are as shown in FIG. 1 and the extraction using the solvent was hardly performed. Only the direct concentration of the sample using the vacuum rotary evaporator showed good results.
실시예 3Example 3
상기 실시예 1, 2를 통하여 얻은 최적의 조건인 트리플루오로무수아세트산 100 ㎕와 트리플루오로에탄올 50 ㎕을 반응시약으로 사용하고 반응시간 60분, 반응온도 80 ℃에서 반응시켜서 얻은 용액을 2 ㎕ 취하여, 기체 크로마토그래피 또는 기체 크로마토그래피/질량분석기등으로 바람직하게는 기체 크로마토그래피/질량분석기에 주입하여 도 2에 나타낸 바와 같이 미량의 3종 제초제의 피크와 내부표준물질의 크로마토그램을 얻었다. 도 3은 유도체화된 3종 산성제초제의 질량스펙트럼을 나타내고 있는데, 유도체화된 각각의 분자량과 특성 토막이온이 잘 나타나고 있다. 이와 같은 3종 산성제초제의 농도를 결정하기 위해 사용된 기기로는 휴렛-팩커드 (Hewlett-Packard)사의 5972 질량분석기와 여기에 연결된 5890 플러스(plus) 기체 크로마토그래피이다. 사용된 이온화 방법은 전자충격법(electron impact, EI)이며 이온원의 온도는 280 ℃이었다. 정량을 위하여 SIM(Selected Ion Monitoring) 모드가 사용되었으며 선택된 이온은 글리포세이트의 경우는 기준 피크(base peak)인 m/z 113이 사용되었으며 엔도탈의 경우는 m/z가 123, 클로람벤은 m/z가 348 이었다. 내부표준물질의 경우는 m/z 159가 사용되었다. 분석에 사용된 분리관 (column)은 길이가 25 m, 내경이 0.25 ㎜, 필름 두께가 0.25 ㎛인 울트라(ultra) 2 컬럼을, 이동상 기체로는 헬륨을 사용하였으며, 흐름 속도는 0.7㎖/min이었다. 컬럼의 온도는 초기에 100 ℃에서 머무른 시간없이 10 ℃/min 속도로 200 ℃까지 승온시키고 다시 20 ℃/min 속도로 300 ℃까지 승온하였다. 시료 주입구의 온도는 250 ℃이었으며 기체크로마토그래프와 질량분석기 연결장치의 온도는 280 ℃이었다.2 μl of the solution obtained by reacting 100 μl of trifluoroanhydric acid and 50 μl of trifluoroethanol, which are the optimum conditions obtained in Examples 1 and 2, as a reaction reagent and reacting at a reaction time of 60 minutes and a reaction temperature of 80 ° C. The mixture was injected into a gas chromatography / mass spectrometer or the like, preferably into a gas chromatography / mass spectrometer to obtain a chromatogram of peaks of three kinds of herbicides and an internal standard as shown in FIG. 2. Figure 3 shows the mass spectrum of the three derivatized acidic herbicides, the molecular weight and characteristic fragment ion of each derivatized. The instrument used to determine the concentration of these three acid herbicides is Hewlett-Packard's 5972 mass spectrometer and 5890 plus gas chromatography connected thereto. The ionization method used was electron impact (EI) and the temperature of the ion source was 280 ° C. SIM (Selected Ion Monitoring) mode was used for quantification, m / z 113, the base peak for glyphosate, 123 for m / z and m for endolam, / z was 348. For internal standards m / z 159 was used. The column used for analysis was an ultra 2 column having a length of 25 m, an inner diameter of 0.25 mm, a film thickness of 0.25 μm, helium as the mobile phase gas, and a flow rate of 0.7 ml / min. It was. The temperature of the column was initially raised to 200 ° C. at a rate of 10 ° C./min without the time of staying at 100 ° C., and again to 300 ° C. at a rate of 20 ° C./min. The temperature of the sample inlet was 250 ° C and the temperature of the gas chromatograph and the mass spectrometer connection device was 280 ° C.
실시예 4Example 4
일부 정수장에서 채취한 시료를 10 ㎖ 취하여 내부표준물질인 2,4-디클로로페닐아세트산 10㎍/㎖를 10㎕ 첨가한 후 진공회전증발기를 이용하여 완전건조시키고 남아 있는 잔류물에 트리플루오로무수아세트산 50 내지 150 ㎕ 바람직하게는 100 ㎕와 트리플루오로에탄올 25 내지 100 ㎕, 바람직하게는 50 ㎕를 첨가하여 60 내지 90 ℃ 바람직하게는 80 ℃에서 30 내지 120 분, 바람직하게는 60분 동안 가열한 후, 반응을 완성시키고 냉각시킨 다음, 다시 질소 하에서 건조시키고 다시 에틸아세테이트 100 ㎕ 로 용해시킨 후 2 ㎕를 직접 기체 크로마토그래피에 주입하여 분석하였다. 이러한 분석방법을 통하여 3종의 제초제를 질량분석기를 사용하여 정량하기 위한 검량곡선은 도 4에 나타낸 바와 같고 0.2 내지 5.0 ㎍/ℓ농도 범위에서 좋은 직선성을 나타냈다.Take 10 ml of sample from some water purification plant, add 10µl of 2,4-dichlorophenylacetic acid as an internal standard, and completely dry it using vacuum rotary evaporator. Trifluoro anhydride is added to the remaining residue. 50 to 150 µl, preferably 100 µl and 25 to 100 µl of trifluoroethanol, preferably 50 µl, are added and heated at 60 to 90 ° C., preferably at 80 ° C., for 30 to 120 minutes, preferably 60 minutes. After completion of the reaction, the reaction was cooled, dried under nitrogen again, dissolved in 100 μl of ethyl acetate, and then 2 μl was directly injected into gas chromatography for analysis. The calibration curve for quantifying the three herbicides using the mass spectrometer through this analytical method is as shown in Figure 4 and showed a good linearity in the concentration range of 0.2 to 5.0 ㎍ / ℓ.
상기 설명한 바와 같이, 본 발명은 동시 추출이 어려운 3종의 제초제를 수질시료 중에서 효과적으로 분석할 수 있도록 하며, 기체 크로마토그래피 또는 기체크로마토그래피/질량분석기에 대해서 선택적이고 우수한 감도를 가진다. 또한, 물질의 분석에 일반적으로 사용되는 기체크로마토그래피/질량분석기로 분석하는 최적의분석조건을 제공한다. 따라서, 본 발명을 이용할 경우, 우수한 감도, 재현성 향상, 정확성, 분석시간의 단축, 저비용 및 간편성 등을 만족시킬 수 있으며, 이로 인해 인체에 유해한 물질인 3종의 제초제를 수질시료에서 동시에 정량적으로 분석할 수 있어 환경시료 특히 수질시료 분석에 폭 넓게 응용할 수 있다.As described above, the present invention makes it possible to effectively analyze three herbicides, which are difficult to co-extract, in water samples, and has selective and excellent sensitivity to gas chromatography or gas chromatography / mass spectrometer. In addition, it provides optimum analysis conditions for analysis with gas chromatography / mass spectrometer which are generally used for analysis of materials. Therefore, when using the present invention, it is possible to satisfy excellent sensitivity, reproducibility improvement, accuracy, shortening of analysis time, low cost and simplicity, and thus quantitatively analyzing three herbicides, which are harmful to the human body, in a water sample at the same time. It can be widely applied to the analysis of environmental samples, especially water samples.
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CN107843664A (en) * | 2017-10-30 | 2018-03-27 | 诺安实力可商品检验(青岛)有限公司 | The assay method of glufosinate-ammonium, glyphosate and its metabolin aminomethyl phosphonic acid residual quantity in tealeaves |
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CN103175908A (en) * | 2013-03-07 | 2013-06-26 | 中国科学院东北地理与农业生态研究所 | Method for determining bensulfuron methyl in water by boron trifluoride derivation-gaschromatographic mass spectrometry method |
CN108593800B (en) * | 2018-04-28 | 2021-11-26 | 杭州医学院 | Method for extracting, purifying and detecting glyphosate content in grains |
CN109212070B (en) * | 2018-09-24 | 2021-05-07 | 丁立平 | Gas chromatography for simultaneously determining four benzoic acid herbicides in grains |
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JPH0792154A (en) * | 1993-09-24 | 1995-04-07 | Shimadzu Corp | Method for analyzing glyphosert in agricultural product |
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