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JPS6148100B2 - - Google Patents
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JPS6148100B2 - - Google Patents

Info

Publication number
JPS6148100B2
JPS6148100B2 JP8341881A JP8341881A JPS6148100B2 JP S6148100 B2 JPS6148100 B2 JP S6148100B2 JP 8341881 A JP8341881 A JP 8341881A JP 8341881 A JP8341881 A JP 8341881A JP S6148100 B2 JPS6148100 B2 JP S6148100B2
Authority
JP
Japan
Prior art keywords
gas
particle separator
cyclone
sample
pipe
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP8341881A
Other languages
Japanese (ja)
Other versions
JPS57198848A (en
Inventor
Koji Okada
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shimadzu Corp
Original Assignee
Shimadzu Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shimadzu Corp filed Critical Shimadzu Corp
Priority to JP8341881A priority Critical patent/JPS57198848A/en
Publication of JPS57198848A publication Critical patent/JPS57198848A/en
Publication of JPS6148100B2 publication Critical patent/JPS6148100B2/ja
Granted legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N1/00Sampling; Preparing specimens for investigation
    • G01N1/02Devices for withdrawing samples
    • G01N1/22Devices for withdrawing samples in the gaseous state
    • G01N1/2202Devices for withdrawing samples in the gaseous state involving separation of sample components during sampling
    • G01N1/2211Devices for withdrawing samples in the gaseous state involving separation of sample components during sampling with cyclones
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N1/00Sampling; Preparing specimens for investigation
    • G01N1/02Devices for withdrawing samples
    • G01N1/22Devices for withdrawing samples in the gaseous state
    • G01N1/2202Devices for withdrawing samples in the gaseous state involving separation of sample components during sampling
    • G01N2001/222Other features
    • G01N2001/2223Other features aerosol sampling devices

Landscapes

  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biomedical Technology (AREA)
  • Molecular Biology (AREA)
  • Physics & Mathematics (AREA)
  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Pathology (AREA)
  • Investigating, Analyzing Materials By Fluorescence Or Luminescence (AREA)

Description

【発明の詳細な説明】 この発明は発光分光分析における固体試料エー
ロゾル発生装置に系るものである。一般に固体試
料からそのエーロゾルを発生する方法としてはア
ーク放電又はスパーク放電などによる気化法が用
いられている。そして発生したエーロゾルは化学
炎、D−Cアークプラズマ、誘導結合プラズマ
(ICP)などの光源によつて励起され分析され
る。この分析法は試料の蒸発過程と励起過程とが
別々に行なわれるため、通常の発光分光分析で問
題となる種々の干渉の原因解明に有効な手だんと
して、あるいは金属業界の異材検出の手段として
研究開発されてきた。しかし従来の装置において
は実用分析装置として使用する場合いくつかの欠
点が指適されていた。それを次にあげる。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a solid sample aerosol generator for emission spectrometry. Generally, a vaporization method using arc discharge or spark discharge is used to generate an aerosol from a solid sample. The generated aerosol is then excited and analyzed by a light source such as a chemical flame, DC arc plasma, or inductively coupled plasma (ICP). In this analysis method, the evaporation process and excitation process of the sample are performed separately, so it is used as an effective method for elucidating the causes of various interferences that occur in ordinary emission spectroscopy, or as a means for detecting foreign materials in the metal industry. has been researched and developed. However, conventional devices exhibit several drawbacks when used as practical analytical devices. I'll give you that next.

(1) 放電により蒸発した試料は放電室内、搬送管
内で凝集し、発光光源に搬送されるまでに0か
ら数百ミクロンまでの粒径分布となる。このう
ち径の大きい粒子は発光々源内では完全に原子
化されないと考えられる。完全に原子化される
粒子に較べ桁違いに多い原子数を持つ大径粒子
が搬送経路中滞留したり、原子化過程で不安定
な動きをすることは粒子数の比率が小さくとも
測光強度を不安定にする要因になる。従来の装
置では、このような粗大化した粒子もすべて発
光々源内に導入していたため分析結果が不安定
で分析精度がよくなかつた。
(1) The sample evaporated by the discharge aggregates in the discharge chamber and the transport tube, and has a particle size distribution ranging from 0 to several hundred microns by the time it is transported to the light source. It is thought that the particles with larger diameters are not completely atomized within the light emitting source. If large-diameter particles with an order of magnitude greater number of atoms than completely atomized particles remain in the transport path or move unstable during the atomization process, the photometric intensity will decrease even if the ratio of the number of particles is small. This can cause instability. In conventional devices, all of these coarse particles were introduced into the luminescent source, resulting in unstable analysis results and poor analysis accuracy.

(2) 従来の装置では試料を気化するための放電室
内に流したガスにより粒子を搬送し、そのまゝ
発光々源に導入する単一流路を用いていたた
め、放電室内、発光々源のガス流量を独立に決
定できなかつた。又放電室内、搬送管内に付着
した粒子を分析ごとに流量を増しておし出す操
作をする際、流量の増加が発光々源の条件によ
り制約をうけ完全に粒子を追い出せず前回試料
の影響が残る可能性が大きかつた。
(2) Conventional devices used a single flow path in which particles were transported by gas flowing into the discharge chamber to vaporize the sample, and introduced directly into the luminescent source. The flow rate could not be determined independently. In addition, when increasing the flow rate for each analysis to release particles that have adhered to the discharge chamber or the transport tube, the increase in flow rate is limited by the conditions of the luminescent source, and the particles cannot be completely expelled, resulting in the influence of the previous sample. There was a strong possibility that he would remain.

この発明はエーロゾル搬送管の末端すなわち発
光々源直前にエーロゾル処理部をつけ、それに対
応するガスコントロール系をもうけることによ
り、上記の問題点を解消するものである。上記(1)
の対策については粒子の凝集はさけられないた
め、搬送後に微細粒子のみとり出すこととし、遠
心分離器(サイクロン)を用いた。上記(2)につい
てはサイクロン部の入口部分、出口部分にそれぞ
れ、混合部、分流部を作り、放電部、発光々源部
にそれぞれ任意のガス流量を選ぶことができるよ
うにした。以下実施例によつてこの発明を説明す
る。
The present invention solves the above-mentioned problems by providing an aerosol treatment section at the end of the aerosol transport tube, that is, immediately before the light emitting source, and providing a corresponding gas control system. Above (1)
As a countermeasure for this, since agglomeration of particles cannot be avoided, it was decided to take out only the fine particles after transportation, and a centrifugal separator (cyclone) was used. Regarding (2) above, a mixing section and a flow dividing section were created at the inlet and outlet sections of the cyclone section, respectively, so that arbitrary gas flow rates could be selected for the discharge section and the light emitting source section, respectively. The present invention will be explained below with reference to Examples.

第1図は本発明の一実施例を示す。Sは放電部
で、こゝでスパーク放電で発生した試料mのエー
ロゾルはステンレス管P中を搬送され、よどみ点
のできないよう同軸二重構造とした混合部Mの中
心管Pmより流入する。そして混合部の外管Pbよ
り流入する希釈用のガスと混合され、サイクロン
Cで必要な流入速度をもつガス流となる。このエ
ーロゾルをサイクロンCの外筒Cb、内筒Ciの間
に接線方向に流入させると試料粒子は旋回をしな
がら下におりてゆく。その時粒子は遠心力とスト
ークスの抵抗をうけ外壁方向にドリフトしてゆ
く。このドリフト速度は粒径に比例するため大き
い粒子ほど壁に到達する時間は短かい。壁に到達
した粒子はダストホールに落ち、到達しなかつた
微細粒子だけが内筒を上がつてゆく。内筒の上部
は分流部となつており、上昇した粒子はよどみ点
ができないように内筒に同軸型に挿入されたセン
ター管Cmをとおり発光光源部Lに導入される。
外筒Cbからとり出されたエーロゾルは調節バル
ブVeを通し排出される。このバルブVeを調節す
ることにより発光々源部Lに導入するエーロゾル
量を調節する。分析ごとに放電部S内、搬送管P
内を清掃する時は希釈ガスとして混合部Mに流し
ていたガスを放電部S内に流しこむ。これは分析
時のガス量に比べ数倍の量にあたり付着した粒子
は実用上問題にならない程度まで流し出される。
この場合も発光々源部Lに流入するガス量は変化
せず悪影響はあたえない。
FIG. 1 shows an embodiment of the invention. S is a discharge section, where the aerosol of the sample m generated by spark discharge is conveyed through a stainless steel tube P, and flows into the central tube Pm of the mixing section M, which has a coaxial double structure to prevent stagnation points. Then, it is mixed with the dilution gas flowing in from the outer pipe Pb of the mixing section, and becomes a gas flow having the required inflow velocity in the cyclone C. When this aerosol flows tangentially between the outer cylinder Cb and the inner cylinder Ci of the cyclone C, the sample particles descend downward while rotating. At that time, the particles drift toward the outer wall due to centrifugal force and Stokes resistance. This drift speed is proportional to the particle size, so the larger the particle, the shorter the time it takes for it to reach the wall. Particles that reach the wall fall into the dust hole, and only the fine particles that do not reach the wall move up the inner cylinder. The upper part of the inner cylinder is a flow dividing part, and the particles that have risen are introduced into the light emitting light source part L through a center tube Cm coaxially inserted into the inner cylinder to prevent the formation of stagnation points.
The aerosol taken out from the outer cylinder Cb is discharged through the control valve Ve. By adjusting this valve Ve, the amount of aerosol introduced into the light emitting source section L is adjusted. Inside the discharge section S and the transport pipe P for each analysis.
When cleaning the inside, the gas that was flowing into the mixing section M as a diluting gas is flowed into the discharge section S. This is several times the amount of gas during analysis, and the attached particles are flushed out to the extent that they do not pose a practical problem.
In this case as well, the amount of gas flowing into the light emitting source section L does not change and there is no adverse effect.

実際に作製したサイクロン部の断面図を第2図
に示す。1は捕獲された粗大粒子のたまるダスト
ホール、2はサイクロン外筒、3はサイクロン内
筒である。4は混合部、5は分流部である。
FIG. 2 shows a cross-sectional view of the cyclone section that was actually produced. 1 is a dust hole where captured coarse particles accumulate, 2 is a cyclone outer cylinder, and 3 is a cyclone inner cylinder. 4 is a mixing section, and 5 is a dividing section.

この装置において処理後のエーロゾル粒径は、
計算値にどおり10μ以下となつた。
In this device, the aerosol particle size after treatment is
The calculated value was less than 10μ.

以上細述したようにサイクロンを使用したこと
により従来そのまゝ発光光源内に導入していた粒
度分布の広いエーロゾルから微細粒のみのエーロ
ゾルを作ることに成功した。又混合部、分流部を
もうけたことにより放電室と発光々源部のガス流
量を独立して決定でき、分析の最適条件を選ぶこ
とが可能になり、大流量のガスによるパージが可
能になつた。そのため従来のエーロゾル発生装置
の難点を解決することができ十分実用分析が可能
となつた。
As described in detail above, by using a cyclone, we succeeded in creating an aerosol containing only fine particles from an aerosol with a wide particle size distribution that was conventionally introduced directly into the light emitting light source. In addition, by providing a mixing section and a dividing section, the gas flow rate in the discharge chamber and the light emitting source section can be determined independently, making it possible to select the optimum conditions for analysis, and making it possible to purge with a large flow rate of gas. Ta. Therefore, the drawbacks of conventional aerosol generators can be solved and practical analysis has become possible.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の一実施例装置の全体を示す配
管図、第2図は同じくサイクロン粒子分別部の縦
断面図である。 S……試料気化用放電部、P……搬送管、M…
…混合部、C……サイクロン、L……試料原子化
光源。
FIG. 1 is a piping diagram showing the entire apparatus of an embodiment of the present invention, and FIG. 2 is a longitudinal sectional view of the cyclone particle separation section. S...Discharge section for sample vaporization, P...Transport tube, M...
...mixing section, C...cyclone, L...sample atomization light source.

Claims (1)

【特許請求の範囲】[Claims] 1 固体試料を気化させる部分と、サイクロン型
粒子分別装置とよりなり、搬送ガスによつて上記
固体試料を気化させる部分で発生した試料蒸気を
上記サイクロン型粒子分別装置に移送させる構成
で、上記試料を移送させる管がサイクロン型粒子
分別装置の作動ガス供給管内に挿入開口させてあ
り、上記サイクロン型粒子分別装置の中心部上方
から抽気するガス管を試料原子化部に導くと共に
上記抽気ガス管の外周に上記粒子分別装置の排気
管を設け、試料蒸気を上記固体試料気化部から上
記粒子分別装置まで搬送するガスの流量、上記粒
子分別装置の作動ガス供給量及び排気ガス量を各
別に調節できるようにしたことを特徴とする固体
エーロゾル発生装置。
1 Consisting of a part that vaporizes the solid sample and a cyclone-type particle separator, the sample vapor generated in the part that vaporizes the solid sample is transferred to the cyclone-type particle separator using a carrier gas, A pipe for transporting the gas is inserted into and opened in the working gas supply pipe of the cyclone-type particle separator, and the gas pipe to bleed air from above the center of the cyclone-type particle separator is guided to the sample atomization section, and the bleed gas pipe is An exhaust pipe of the particle separator is provided on the outer periphery, and the flow rate of gas for conveying the sample vapor from the solid sample vaporizer to the particle separator, the amount of working gas supplied to the particle separator, and the amount of exhaust gas can be adjusted individually. A solid aerosol generator characterized by:
JP8341881A 1981-05-30 1981-05-30 Producing apparatus for solid aerosol Granted JPS57198848A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8341881A JPS57198848A (en) 1981-05-30 1981-05-30 Producing apparatus for solid aerosol

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8341881A JPS57198848A (en) 1981-05-30 1981-05-30 Producing apparatus for solid aerosol

Publications (2)

Publication Number Publication Date
JPS57198848A JPS57198848A (en) 1982-12-06
JPS6148100B2 true JPS6148100B2 (en) 1986-10-22

Family

ID=13801884

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8341881A Granted JPS57198848A (en) 1981-05-30 1981-05-30 Producing apparatus for solid aerosol

Country Status (1)

Country Link
JP (1) JPS57198848A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104865106B (en) * 2015-06-15 2017-06-20 华北电力大学(保定) A kind of microbial aerosol sampling apparatus

Also Published As

Publication number Publication date
JPS57198848A (en) 1982-12-06

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