JP2011242401A - Column - Google Patents
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- JP2011242401A JP2011242401A JP2011168065A JP2011168065A JP2011242401A JP 2011242401 A JP2011242401 A JP 2011242401A JP 2011168065 A JP2011168065 A JP 2011168065A JP 2011168065 A JP2011168065 A JP 2011168065A JP 2011242401 A JP2011242401 A JP 2011242401A
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- 239000000126 substance Substances 0.000 claims abstract description 43
- 239000002253 acid Substances 0.000 claims abstract description 19
- 239000003463 adsorbent Substances 0.000 claims abstract description 19
- 239000000463 material Substances 0.000 claims abstract description 13
- 239000011800 void material Substances 0.000 claims abstract description 8
- 239000002245 particle Substances 0.000 claims abstract description 6
- 239000000945 filler Substances 0.000 claims abstract description 5
- 238000001179 sorption measurement Methods 0.000 claims description 19
- 239000002585 base Substances 0.000 claims description 16
- 229910000288 alkali metal carbonate Inorganic materials 0.000 claims description 4
- 150000008041 alkali metal carbonates Chemical class 0.000 claims description 4
- 150000008044 alkali metal hydroxides Chemical class 0.000 claims description 4
- 150000001412 amines Chemical class 0.000 claims description 4
- 150000003868 ammonium compounds Chemical class 0.000 claims description 4
- 150000001875 compounds Chemical class 0.000 claims description 4
- 238000000034 method Methods 0.000 abstract description 16
- 239000003344 environmental pollutant Substances 0.000 abstract description 7
- 231100000719 pollutant Toxicity 0.000 abstract description 7
- 239000007789 gas Substances 0.000 description 40
- 239000000758 substrate Substances 0.000 description 15
- 238000011109 contamination Methods 0.000 description 13
- 239000000243 solution Substances 0.000 description 13
- 238000004458 analytical method Methods 0.000 description 11
- 239000000356 contaminant Substances 0.000 description 9
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 8
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 238000011156 evaluation Methods 0.000 description 6
- 238000012856 packing Methods 0.000 description 6
- 239000002904 solvent Substances 0.000 description 6
- 238000000638 solvent extraction Methods 0.000 description 6
- 238000005273 aeration Methods 0.000 description 5
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 4
- AFVFQIVMOAPDHO-UHFFFAOYSA-N Methanesulfonic acid Chemical compound CS(O)(=O)=O AFVFQIVMOAPDHO-UHFFFAOYSA-N 0.000 description 4
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 4
- -1 and a magnetic disk Substances 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- OFOBLEOULBTSOW-UHFFFAOYSA-N Propanedioic acid Natural products OC(=O)CC(O)=O OFOBLEOULBTSOW-UHFFFAOYSA-N 0.000 description 3
- DNIAPMSPPWPWGF-UHFFFAOYSA-N Propylene glycol Chemical compound CC(O)CO DNIAPMSPPWPWGF-UHFFFAOYSA-N 0.000 description 3
- ZMANZCXQSJIPKH-UHFFFAOYSA-N Triethylamine Chemical compound CCN(CC)CC ZMANZCXQSJIPKH-UHFFFAOYSA-N 0.000 description 3
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 3
- 238000004255 ion exchange chromatography Methods 0.000 description 3
- 238000000691 measurement method Methods 0.000 description 3
- 230000035945 sensitivity Effects 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- DDFHBQSCUXNBSA-UHFFFAOYSA-N 5-(5-carboxythiophen-2-yl)thiophene-2-carboxylic acid Chemical compound S1C(C(=O)O)=CC=C1C1=CC=C(C(O)=O)S1 DDFHBQSCUXNBSA-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 2
- USFZMSVCRYTOJT-UHFFFAOYSA-N Ammonium acetate Chemical compound N.CC(O)=O USFZMSVCRYTOJT-UHFFFAOYSA-N 0.000 description 2
- 239000005695 Ammonium acetate Substances 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 2
- GSEJCLTVZPLZKY-UHFFFAOYSA-N Triethanolamine Chemical compound OCCN(CCO)CCO GSEJCLTVZPLZKY-UHFFFAOYSA-N 0.000 description 2
- 235000019257 ammonium acetate Nutrition 0.000 description 2
- 229940043376 ammonium acetate Drugs 0.000 description 2
- VZTDIZULWFCMLS-UHFFFAOYSA-N ammonium formate Chemical compound [NH4+].[O-]C=O VZTDIZULWFCMLS-UHFFFAOYSA-N 0.000 description 2
- 230000003749 cleanliness Effects 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 235000011187 glycerol Nutrition 0.000 description 2
- 239000003906 humectant Substances 0.000 description 2
- 150000007529 inorganic bases Chemical class 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229940098779 methanesulfonic acid Drugs 0.000 description 2
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 description 2
- 150000007522 mineralic acids Chemical class 0.000 description 2
- 150000007524 organic acids Chemical class 0.000 description 2
- 150000007530 organic bases Chemical class 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 239000010453 quartz Substances 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 229910000029 sodium carbonate Inorganic materials 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- 239000013076 target substance Substances 0.000 description 2
- VDZOOKBUILJEDG-UHFFFAOYSA-M tetrabutylammonium hydroxide Chemical compound [OH-].CCCC[N+](CCCC)(CCCC)CCCC VDZOOKBUILJEDG-UHFFFAOYSA-M 0.000 description 2
- WGTYBPLFGIVFAS-UHFFFAOYSA-M tetramethylammonium hydroxide Chemical compound [OH-].C[N+](C)(C)C WGTYBPLFGIVFAS-UHFFFAOYSA-M 0.000 description 2
- GETQZCLCWQTVFV-UHFFFAOYSA-N trimethylamine Chemical compound CN(C)C GETQZCLCWQTVFV-UHFFFAOYSA-N 0.000 description 2
- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 239000004696 Poly ether ether ketone Substances 0.000 description 1
- 239000002202 Polyethylene glycol Substances 0.000 description 1
- 239000006004 Quartz sand Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 238000005349 anion exchange Methods 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 238000005341 cation exchange Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000003480 eluent Substances 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 235000019253 formic acid Nutrition 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 238000004811 liquid chromatography Methods 0.000 description 1
- 239000004973 liquid crystal related substance Substances 0.000 description 1
- VZCYOOQTPOCHFL-UPHRSURJSA-N maleic acid Chemical compound OC(=O)\C=C/C(O)=O VZCYOOQTPOCHFL-UPHRSURJSA-N 0.000 description 1
- 239000011976 maleic acid Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 229920001515 polyalkylene glycol Polymers 0.000 description 1
- 229920006122 polyamide resin Polymers 0.000 description 1
- 229920005668 polycarbonate resin Polymers 0.000 description 1
- 239000004431 polycarbonate resin Substances 0.000 description 1
- 229920002530 polyetherether ketone Polymers 0.000 description 1
- 229920001223 polyethylene glycol Polymers 0.000 description 1
- 229920001451 polypropylene glycol Polymers 0.000 description 1
- 229920005990 polystyrene resin Polymers 0.000 description 1
- 239000011736 potassium bicarbonate Substances 0.000 description 1
- 229910000028 potassium bicarbonate Inorganic materials 0.000 description 1
- 235000015497 potassium bicarbonate Nutrition 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 235000011181 potassium carbonates Nutrition 0.000 description 1
- TYJJADVDDVDEDZ-UHFFFAOYSA-M potassium hydrogencarbonate Chemical compound [K+].OC([O-])=O TYJJADVDDVDEDZ-UHFFFAOYSA-M 0.000 description 1
- 229940086066 potassium hydrogencarbonate Drugs 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
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- 238000004366 reverse phase liquid chromatography Methods 0.000 description 1
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- 238000012216 screening Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 235000017550 sodium carbonate Nutrition 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- UUCCCPNEFXQJEL-UHFFFAOYSA-L strontium dihydroxide Chemical compound [OH-].[OH-].[Sr+2] UUCCCPNEFXQJEL-UHFFFAOYSA-L 0.000 description 1
- 229910001866 strontium hydroxide Inorganic materials 0.000 description 1
- 150000005846 sugar alcohols Polymers 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- VZCYOOQTPOCHFL-UHFFFAOYSA-N trans-butenedioic acid Natural products OC(=O)C=CC(O)=O VZCYOOQTPOCHFL-UHFFFAOYSA-N 0.000 description 1
- 229910021642 ultra pure water Inorganic materials 0.000 description 1
- 239000012498 ultrapure water Substances 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
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Abstract
Description
本発明は、酸物質または塩基物質を含む気体吸着用カラムに関するものである。 The present invention relates to a gas adsorption column containing an acid substance or a base substance.
半導体ウェーハ、液晶基板、磁気ディスク等の電子基板(以下、基板と称する。)を製造する環境においては、その製造空間中の酸物質、塩基物質等の汚染物質が基板に吸着する等して、製品の歩留まりの低下や品質の低下が生ずることから、このような基板を製造する工程は、クリーンルームで行われている。そして、各製造過程でのクリーンルームにおける上記の酸物質、塩基物質等による汚染状態を評価することが必要であるところ、その手法としては、例えば、吸引ポンプで吸引したクリーンルーム内の空気を一定の流量で吸収溶液に通し、該空気中の汚染物質を吸収させ、吸収された汚染物質を分析する方法、あるいは、吸引ポンプで吸引したクリーンルーム内の空気を一定の流量でフィルターに通し、該空気中の汚染物質を吸着させ、フィルターから汚染物質を溶媒により脱離させ、脱離された汚染物質を分析する方法などが提案されている(例えば、非特許文献1、2、特許文献1参照。)。
In an environment for manufacturing an electronic substrate (hereinafter referred to as a substrate) such as a semiconductor wafer, a liquid crystal substrate, and a magnetic disk, contaminants such as acid substances and base substances in the manufacturing space are adsorbed on the substrate, Since the yield of products and the quality are lowered, the process of manufacturing such a substrate is performed in a clean room. In addition, it is necessary to evaluate the contamination state due to the above-mentioned acid substances, base substances, etc. in the clean room in each manufacturing process. For example, as the technique, air in the clean room sucked by a suction pump is flowed at a constant flow rate. In this method, the pollutant in the air is absorbed and the absorbed pollutant is analyzed, or the air in the clean room sucked by the suction pump is passed through the filter at a constant flow rate. A method of adsorbing contaminants, desorbing contaminants from a filter with a solvent, and analyzing the desorbed contaminants has been proposed (see, for example,
近年、クリーンルームには、より高度な洗浄空間の確保が求められており、それに伴って、酸または塩基による汚染状態をより高感度で評価する方法が求められている。 In recent years, a clean room has been required to secure a more sophisticated cleaning space, and accordingly, a method for evaluating a contamination state due to an acid or a base with higher sensitivity is required.
しかしながら、従来の気体の汚染状態の評価方法では、気中の汚染物質の濃度が低い場合、吸収溶液などを濃縮して分析を行っていたが、濃縮液を全量分析に付すること、すなわち、吸収溶液に吸収された汚染物質を全量分析に付することは難しく、高感度の評価という観点で、十分満足のいくものではなかった。また、吸収溶液を用いた評価方法では、吸収溶液によるクリーンルームの汚染の可能性があった。 However, in the conventional method for evaluating the state of contamination of gas, when the concentration of pollutants in the air is low, the analysis is performed by concentrating the absorbing solution, etc., but the concentrated solution is subjected to the total amount analysis, It was difficult to subject the pollutant absorbed in the absorbing solution to the total amount analysis, which was not satisfactory from the viewpoint of high sensitivity evaluation. Further, in the evaluation method using the absorbing solution, there is a possibility of contamination of the clean room by the absorbing solution.
かかる状況のもと、上記課題に応えるべく鋭意検討した結果、特定のカラムを用いて気中の酸物質や塩基物質などの汚染物質を吸着させ、該カラムに吸着された汚染物質をオンラインで溶媒抽出して分析することにより、気中の汚染物質をサンプリングするに際して吸収溶液を用いることなく、汚染状態を簡便に、また精度よく評価し得ることを見出し、本発明を完成するに至った。 Under such circumstances, as a result of intensive investigations to meet the above-mentioned problems, a specific column is used to adsorb pollutants such as acid substances and base substances in the air, and the pollutants adsorbed on the column are solvent-solved online. By extracting and analyzing, the present inventors have found that the contamination state can be evaluated easily and accurately without using an absorbing solution when sampling contaminants in the air, and the present invention has been completed.
すなわち、本発明は、平均粒径または断面平均直径が500μm〜1000μmである基材に、吸着剤が保持されてなる充填剤が充填されたカラムであって、当該カラムの空隙容積が5〜100μlである気体吸着用カラムにかかるものである。 That is, the present invention is a column in which a base material having an average particle diameter or a cross-sectional average diameter of 500 μm to 1000 μm is packed with a filler in which an adsorbent is held, and the void volume of the column is 5 to 100 μl. It is applied to the gas adsorption column.
また、本発明は、上記カラムに評価対象の気体を通気することにより、該気体に含まれる酸物質または塩基物質をカラム内の充填剤に吸着させ、夫々、吸着された酸物質または塩基物質をオンラインで溶媒抽出して分析する気体の汚染状態の評価方法にかかるものである。 Further, the present invention allows the gas to be evaluated to pass through the column so that the acid substance or base substance contained in the gas is adsorbed to the filler in the column, and the adsorbed acid substance or base substance is respectively adsorbed. The present invention relates to a method for evaluating the contamination state of a gas that is analyzed by extracting a solvent online.
また、本発明は、上記カラムに評価対象の気体を通気することにより、該気体に含まれる酸物質をカラム内の充填剤に吸着させ、吸着された酸物質をオンラインで溶媒抽出して分析する気体の汚染状態の評価方法にかかるものである。 In the present invention, the gas to be evaluated is passed through the column so that the acid substance contained in the gas is adsorbed to the packing material in the column, and the adsorbed acid substance is subjected to solvent extraction online for analysis. This is a method for evaluating the state of gas contamination.
また、本発明は、上記カラムに評価対象の気体を通気することにより、該気体に含まれる塩基物質をカラム内の充填剤に吸着させ、吸着された塩基物質をオンラインで溶媒抽出して分析する気体の汚染状態の評価方法にかかるものである。 In the present invention, the gas to be evaluated is passed through the column so that the basic substance contained in the gas is adsorbed to the packing material in the column, and the adsorbed basic substance is subjected to solvent extraction online for analysis. This is a method for evaluating the state of gas contamination.
本発明により、酸物質や塩基物質による気体の汚染状態を、高感度で評価することができ、また、吸収溶液を用いることなく評価することができる。 According to the present invention, the state of gas contamination by acid substances and base substances can be evaluated with high sensitivity, and can be evaluated without using an absorbing solution.
本発明のカラムは、基材に吸着剤が保持されてなる充填剤が充填されたカラムである。 The column of the present invention is a column filled with a filler in which an adsorbent is held on a base material.
基材の材質としては、ガラス、石英、ポリカーボネート樹脂、ポリスチレン樹脂、ポリアミド樹脂等があげられる。好ましくは、ガラスまたは石英である。 Examples of the material for the substrate include glass, quartz, polycarbonate resin, polystyrene resin, polyamide resin, and the like. Preferably, it is glass or quartz.
基材の形状としては、表面積の大きな形状が好ましく、粒子状、繊維状等があげられる。好ましくは、粒子状である。 The shape of the substrate is preferably a shape having a large surface area, and examples thereof include particles and fibers. Preferably, it is particulate.
基材の平均粒径または基材の断面平均直径は、通気効率を高める観点から、好ましくは500μm以上であり、より好ましくは600μm以上である。また、捕集効率を高める観点から、好ましくは1000μm以下であり、より好ましくは850μm以下である。なお、このときの測定法はJIS K0069「化学製品のふるい分け試験方法」によるものである。 The average particle diameter of the substrate or the average cross-sectional diameter of the substrate is preferably 500 μm or more, and more preferably 600 μm or more, from the viewpoint of increasing the ventilation efficiency. Moreover, from a viewpoint of improving collection efficiency, Preferably it is 1000 micrometers or less, More preferably, it is 850 micrometers or less. The measurement method at this time is based on JIS K0069 “Chemical product screening test method”.
吸着剤としては、塩基物質または酸物質が用いられる。 As the adsorbent, a basic substance or an acid substance is used.
吸着剤として用いられる塩基物質としては、無機塩基および有機塩基をあげることができる。無機塩基としては、アルカリ金属の炭酸塩、アルカリ金属の水酸化物等をあげることができ、有機塩基としては、アミン、アンモニウム化合物等をあげることができる。 Examples of the basic substance used as the adsorbent include inorganic bases and organic bases. Examples of the inorganic base include alkali metal carbonates and alkali metal hydroxides, and examples of the organic base include amines and ammonium compounds.
吸着剤として用いる塩基物質としては、好ましくは、アルカリ金属の炭酸塩、アルカリ金属の水酸化物、アミンおよびアンモニウム化合物からなる群から選ばれる少なくとも1種の化合物である。 The basic substance used as the adsorbent is preferably at least one compound selected from the group consisting of alkali metal carbonates, alkali metal hydroxides, amines and ammonium compounds.
該アルカリ金属の炭酸塩としては、炭酸ナトリウム、炭酸カリウム、炭酸水素カリウム等があげられる。該アルカリ金属の水酸化物としては、水酸化ストロンチウム、水酸化カリウム、水酸化ナトリウム等があげられる。該アミンとしては、トリエタノールアミン等があげられる。該アンモニウム化合物としては、水酸化テトラメチルアンモニウム、水酸化テトラブチルアンモニウム等があげられる。 Examples of the alkali metal carbonate include sodium carbonate, potassium carbonate, potassium hydrogen carbonate and the like. Examples of the alkali metal hydroxide include strontium hydroxide, potassium hydroxide, and sodium hydroxide. Examples of the amine include triethanolamine. Examples of the ammonium compound include tetramethylammonium hydroxide and tetrabutylammonium hydroxide.
吸着剤として用いる塩基物質としては、より好ましくは、炭酸ナトリウム、水酸化ナトリウムおよびトリエタノールアミンからなる群から選ばれる少なくとも1種の化合物である。 More preferably, the basic substance used as the adsorbent is at least one compound selected from the group consisting of sodium carbonate, sodium hydroxide and triethanolamine.
吸着剤として用いられる酸物質としては、無機酸および有機酸をあげることができる。 Examples of the acid substance used as the adsorbent include inorganic acids and organic acids.
該無機酸としては、硫酸、リン酸等があげられる。該有機酸としては、メタンスルホン酸、マレイン酸、マロン酸等があげられる。 Examples of the inorganic acid include sulfuric acid and phosphoric acid. Examples of the organic acid include methanesulfonic acid, maleic acid, malonic acid and the like.
吸着剤として用いる酸物質としては、好ましくは、硫酸、リン酸およびメタンスルホン酸からなる群から選ばれる少なくとも1種の化合物である。 The acid substance used as the adsorbent is preferably at least one compound selected from the group consisting of sulfuric acid, phosphoric acid and methanesulfonic acid.
吸着剤を基材に保持させる方法としては、吸着剤が固体状の物質の場合は、これを溶媒に溶解して溶液とし、該溶液を基材に塗布するか、または、該溶液に基材を浸漬し、溶媒を乾燥する方法、吸着剤が液状の物質の場合は、そのまま、あるいは、これを溶媒に溶解して溶液とし、該溶液を基材に塗布するか、または基材を浸漬し、溶媒を乾燥する方法等があげられる。 As a method for holding the adsorbent on the substrate, when the adsorbent is a solid substance, dissolve it in a solvent to form a solution, and apply the solution to the substrate, or apply the solution to the substrate. In the case where the adsorbent is a liquid substance, the solution is dissolved in a solvent to form a solution and the solution is applied to the substrate, or the substrate is immersed. And a method of drying the solvent.
また、基材には、吸着剤に加えて保湿剤を塗布していてもよい。該保湿剤としては、エチレングリコール、プロピレングリコール、グリセリンなどの多価アルコール;ポリエチレングリコール、ポリプロピレングリコールなどのポリアルキレングリコールを例示することができる。 In addition to the adsorbent, a humectant may be applied to the substrate. Examples of the humectant include polyhydric alcohols such as ethylene glycol, propylene glycol and glycerin; polyalkylene glycols such as polyethylene glycol and polypropylene glycol.
カラムは、分析の対象となる酸物質・塩基物質の分析に影響を与えない材質からなり、また、10MPa程度の圧力に耐える耐圧性のあるものが好ましい。カラムの材質としては、通常、ステンレス、ポリエーテルエーテルケトン樹脂などが用いられる。また、カラムの形状としては、通常、円筒型のものが使用され、好ましくは、カラムボディ、フリット、スリーブおよびエンドフィッティングからなるカラムであり、例えば、特開2001−249120号公報に記載されたものをあげることができる。 The column is preferably made of a material that does not affect the analysis of the acid substance / base substance to be analyzed, and has a pressure resistance that can withstand a pressure of about 10 MPa. As the material of the column, stainless steel, polyether ether ketone resin or the like is usually used. In addition, the column shape is usually a cylindrical shape, preferably a column body, a frit, a sleeve, and an end fitting, such as those described in JP-A-2001-249120. Can give.
カラムの容積は、分析処理量に対応して適切な大きさのものを使用できる。カラム容積は、通常、0.1ml〜0.5mlであり、好ましくは、0.2ml〜0.3mlである。 The column volume can be appropriately sized according to the analytical throughput. The column volume is usually 0.1 ml to 0.5 ml, preferably 0.2 ml to 0.3 ml.
充填剤を充填後のカラムの空隙容積は、5μl〜100μlであり、該空隙容積が小さすぎると、カラムへの気体の通気速度が低くなること、吸引ポンプにより通気を行った場合に吸引ポンプの負荷が高くなることがある。また、該空隙容積が大きすぎると、オンライン抽出の際にカラムからでる気泡により、測定装置の分離カラムが乾燥劣化することがある。カラムの空隙容積は、好ましくは、10μl〜50μlである。なお、該空隙容積には、配管を接続する部位の容積は、例えば、カラムボディ、フリット、スリーブおよびエンドフィッティングからなるカラムの場合、配管と接続するためにエンドフィッティングやカラムボディに設けられた雌ねじ部の容積は含まない。 The void volume of the column after packing with the packing material is 5 μl to 100 μl. If the void volume is too small, the gas aeration rate to the column will be low, and if the aeration pump is used to vent the suction pump, The load may be high. In addition, if the void volume is too large, the separation column of the measuring apparatus may be deteriorated by drying due to bubbles generated from the column during online extraction. The void volume of the column is preferably 10 μl to 50 μl. Note that the volume of the part to which the pipe is connected is, for example, in the case of a column comprising a column body, frit, sleeve and end fitting, the internal thread provided in the end fitting or the column body for connection to the pipe. The volume of the part is not included.
本発明の評価方法では、評価対象となる気体の酸物質や塩基物質の量を評価するに際し、評価対象の気体をカラムに通気することにより、評価対象の気体中に含まれる酸物質や塩基物質がカラム内の充填剤に吸着される。通気は、通常吸引ポンプを用いて行われる。通気速度は、好ましくは0.1〜2L/分である。通気時間は、好ましくは、数分〜24時間である。 In the evaluation method of the present invention, when evaluating the amount of the gas acid substance or base substance to be evaluated, by passing the gas to be evaluated through the column, the acid substance or base substance contained in the gas to be evaluated Is adsorbed by the packing material in the column. Aeration is usually performed using a suction pump. The aeration rate is preferably 0.1 to 2 L / min. The aeration time is preferably several minutes to 24 hours.
カラムへの評価対象の気体の通気は、通常、クリーンルームやクリーンブースなどの評価対象の空間で行われる。カラムの輸送は、分析対象物質の汚染の無い栓でカラムの口を密封して、および/または、分析対象物質の汚染の無い密閉容器に収納して行う。 The gas to be evaluated is passed through the column in a space to be evaluated such as a clean room or a clean booth. The column is transported by sealing the opening of the column with a stopper free of contamination of the analysis target substance and / or storing it in a sealed container free of contamination of the analysis target substance.
評価対象の気体を通気させた後のカラムは、測定装置に接続され、オンラインで溶媒抽出することにより、充填剤から汚染物質が抽出され、該抽出液を全量分析して、気体の汚染状態の評価を行う。ここで、オンラインで溶剤抽出するとは、評価対象の気体を通気させた後のカラムと分析カラムとが同一ラインに直列で接続されていることにより、例えば、分析カラムに抽出液を送液するポンプと分析カラムとの間に、評価対象の気体を通気させた後のカラムを接続することにより、抽出液が該カラムに流入し、該抽出液により抽出された汚染物質を含む抽出液が分析カラムに導入される形態をいう。 The column after the gas to be evaluated is vented is connected to a measuring device, and by online solvent extraction, contaminants are extracted from the packing material. Evaluate. Here, online solvent extraction means that the column after the gas to be evaluated is vented and the analytical column are connected in series in the same line, for example, a pump that sends the extract to the analytical column By connecting the column after the gas to be evaluated is passed between the gas and the analytical column, the extract flows into the column, and the extract containing the contaminant extracted by the extract is analyzed. Refers to the form introduced in
抽出液の分析は、通常、液体クロマトグラフ法により行われ、イオン交換カラムを用いた陰イオン交換方式、陽イオン交換方式、またはサプレッサーを用いたサプレッサー方式のイオンクロマトグラフ法や、ODSカラムを用いる逆相クロマトグラフ法などがあげられる。 The analysis of the extract is usually carried out by liquid chromatography, using an anion exchange method using an ion exchange column, a cation exchange method, a suppressor method ion chromatography method using a suppressor, or an ODS column. Examples include reverse phase chromatography.
オンラインで溶媒抽出し、抽出液の全量を測定装置に送液するための装置としては、送液ポンプと4方バルブとを有する図1に示す構成の装置をあげることができる。気体吸着用カラムを接続していない状態の装置は、図2に示す構成となる。この図2の構成から4方バルブを切り替えて気体吸着用カラムを装置に接続して、図3に示す構成とする。測定時には、4方バルブを切り替えて図1に示す構成とする。 As an apparatus for performing solvent extraction online and sending the entire amount of the extract to the measuring apparatus, an apparatus having a configuration shown in FIG. 1 having a liquid feed pump and a four-way valve can be given. The apparatus without the gas adsorption column connected has the configuration shown in FIG. The four-way valve is switched from the configuration of FIG. 2 to connect the gas adsorption column to the apparatus, and the configuration shown in FIG. 3 is obtained. At the time of measurement, the four-way valve is switched to the configuration shown in FIG.
分析対象物質の酸物質としては、塩化水素、硝酸、硫酸、リン酸、フッ化水素酸、ギ酸、酢酸等の酸そのものの他、フッ化アンモニウム、ギ酸アンモニウム、酢酸アンモニウム等があげられる。また、分析対象物質の塩基物質としては、アンモニア、トリメチルアミン、トリエチルアミン、アルカノールアミン等の塩基そのものの他、フッ化アンモニウム、ギ酸アンモニウム、酢酸アンモニウム等があげられる。 Examples of the acid substance to be analyzed include hydrogen chloride, nitric acid, sulfuric acid, phosphoric acid, hydrofluoric acid, formic acid, acetic acid and the like, as well as ammonium fluoride, ammonium formate, ammonium acetate, and the like. In addition, examples of the base substance to be analyzed include bases such as ammonia, trimethylamine, triethylamine, and alkanolamine, as well as ammonium fluoride, ammonium formate, and ammonium acetate.
評価対象の空間としては、クリーンルーム、クリーンブースをあげることができる。また、SEMI(Semiconductor Equipment and Materials International)規格に定められたEFEM(Equipment Front End Module)、FOUP(Front Opening Unified Pod)、SMIF(Standard Mechanical Interface )ポッド等もあげることができる。 Clean rooms and clean booths can be listed as evaluation target spaces. In addition, EFEM (Equipment Front End Module), FOUP (Front Opening Unified Pod), SMIF (Standard Mechanical Interface) pod, etc., which are defined in SEMI (Semiconductor Equipment and Materials International) standard, can also be mentioned.
本発明を、実施例によりさらに詳しく説明する。 The invention is explained in more detail by means of examples.
実施例1
(気体吸着用カラムの準備)
粒径600〜850μmの粒子状の石英砂を内容積0.27mlのステンレス製カラムに充填し、カラム内部に超純水を通液してカラム内部の洗浄を行った。次に、硫酸とグリセリンの混合水溶液をカラム内部に通液し、窒素を通気して溶媒を乾燥し、気体吸着用カラムとした。この気体吸着用カラムの空隙容積は、45μlであった。
Example 1
(Preparation of gas adsorption column)
Particulate quartz sand having a particle size of 600 to 850 μm was packed in a stainless steel column having an internal volume of 0.27 ml, and ultrapure water was passed through the column to wash the inside of the column. Next, a mixed aqueous solution of sulfuric acid and glycerin was passed through the inside of the column, nitrogen was passed through to dry the solvent, and a gas adsorption column was obtained. The void volume of this gas adsorption column was 45 μl.
(実験室の汚染状態の評価)
気体吸着用カラムにガス吸引ポンプを接続し、吸引速度0.5L/分で1時間、実験室内の空気を気体吸着用カラムに通気した。次に、気体吸着用カラムを、イオンクロマトグラフに接続し、気体吸着用カラム内の吸着剤に吸着したアンモニウムをオンラインで溶媒抽出し、イオンクロマトグラフによりアンモニウムイオンの付着量を測定した。分析結果を表1に示す。
(Evaluation of laboratory contamination)
A gas suction pump was connected to the gas adsorption column, and air in the laboratory was passed through the gas adsorption column at a suction speed of 0.5 L / min for 1 hour. Next, the gas adsorption column was connected to an ion chromatograph, the ammonium adsorbed on the adsorbent in the gas adsorption column was solvent-extracted online, and the amount of ammonium ions deposited was measured by ion chromatography. The analysis results are shown in Table 1.
実施例2
(クリーンブースの汚染状態の評価)
実施例1と同様にして調製した気体吸着用カラムにガス吸引ポンプを接続し、吸引速度0.5L/分で24時間、実験室に設置したクリーンブース内の空気を気体吸着用カラムに通気した。次に、気体吸着用カラムを、イオンクロマトグラフに接続し、気体吸着用カラム内の吸着剤に吸着したアンモニウムをオンラインで溶媒抽出し、イオンクロマトグラフによりアンモニウムイオンの付着量を測定した。分析結果を表1に示す。
Example 2
(Evaluation of clean booth contamination)
A gas suction pump was connected to the gas adsorption column prepared in the same manner as in Example 1, and the air in the clean booth installed in the laboratory was vented to the gas adsorption column at a suction speed of 0.5 L / min for 24 hours. . Next, the gas adsorption column was connected to an ion chromatograph, the ammonium adsorbed on the adsorbent in the gas adsorption column was solvent-extracted online, and the amount of ammonium ions deposited was measured by ion chromatography. The analysis results are shown in Table 1.
1:溶離液
2:ポンプ
3:4方バルブ
4:分離カラム
5:気体吸着用カラム
1: Eluent 2: Pump 3: Four-way valve 4: Separation column 5: Gas adsorption column
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