JPH0452892B2 - - Google Patents

Info

Publication number
JPH0452892B2
JPH0452892B2 JP22645883A JP22645883A JPH0452892B2 JP H0452892 B2 JPH0452892 B2 JP H0452892B2 JP 22645883 A JP22645883 A JP 22645883A JP 22645883 A JP22645883 A JP 22645883A JP H0452892 B2 JPH0452892 B2 JP H0452892B2
Authority
JP
Japan
Prior art keywords
ozone
introduction tube
pipe
reaction chamber
nitrogen monoxide
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
JP22645883A
Other languages
Japanese (ja)
Other versions
JPS60119445A (en
Inventor
Choku Tsuruta
Takao Shitaya
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 JP22645883A priority Critical patent/JPS60119445A/en
Publication of JPS60119445A publication Critical patent/JPS60119445A/en
Publication of JPH0452892B2 publication Critical patent/JPH0452892B2/ja
Granted legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/76Chemiluminescence; Bioluminescence
    • G01N21/766Chemiluminescence; Bioluminescence of gases

Landscapes

  • Physics & Mathematics (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Plasma & Fusion (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Pathology (AREA)
  • Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)

Description

【発明の詳細な説明】 (イ) 産業上の利用分野 本発明は、例えば自動車の排気ガスや煙道排ガ
スなどに含まれる一酸化窒素の濃度を化学発光式
分析法により分析する化学発光分析計に関し、特
に一酸化窒素とオゾンが反応し、電子励起された
状態の二酸化窒素が基底状態に移る際の発光を測
定する化学発光式分析計に関するものである。
[Detailed Description of the Invention] (a) Industrial Application Field The present invention relates to a chemiluminescence spectrometer that analyzes the concentration of nitrogen monoxide contained in, for example, automobile exhaust gas or flue gas by chemiluminescence analysis. In particular, the present invention relates to a chemiluminescent analyzer that measures luminescence when nitrogen monoxide reacts with ozone and nitrogen dioxide in an electronically excited state shifts to the ground state.

(ロ) 従来技術 例えば自動車の排気ガスや煙道排ガスなどに含
まれる一酸化窒素濃度の測定には、赤外線吸収法
を利用するものや化学発光法によるものが使用さ
れている。
(b) Prior Art For example, methods using infrared absorption method and chemiluminescence method are used to measure the concentration of nitrogen monoxide contained in automobile exhaust gas, flue gas, etc.

化学発光法による分析計は、一酸化窒素に対し
すぐれた選択特性を有し、大きな関心を集めてい
る。この分析計は、その化学発光反応室において
一酸化窒素(NO)とオゾン(O3)とが反応し
(NO+O3→NO2※+O2)、この時に生じる電子励
起された状態の二酸化窒素(NO2※)が基底状
態に移る際(NO2※→NO2+hν)に生じる発光
(hν)強度を測定し、一酸化窒素の量を測定する
ものである。
Analyzers based on chemiluminescence have excellent selective properties for nitric oxide and are attracting great interest. This analyzer reacts with nitric oxide (NO) and ozone (O 3 ) in its chemiluminescent reaction chamber (NO+O 3 →NO 2 *+O 2 ), and the electronically excited state of nitrogen dioxide ( The amount of nitrogen monoxide is measured by measuring the intensity of the light emission (hν) that occurs when NO 2 *) transitions to the ground state (NO 2 *→NO 2 + hν).

この分析計に使用される化学発光反応室の代表
的な従来例を第1図により説明すると、1は外部
からの光の入射を遮断するためのステンレス製の
化学発光反応室であり、2はオゾンを化学発光反
応室1に導入させるパイプであり、3は測定しよ
うとする一酸化窒素を包含するガスを同様に化学
発光反応室1に導入させるパイプである。そし
て、これらのパイプ2と3の端部は、これらのパ
イプから排出されるオゾンと一酸化窒素とが接
触、混合するように内側に曲げられている。6は
ガラス窓で、化学発光反応室1に対しパツキン7
を介し、下図示のねじなどの固定部材により固定
されている。このガラス窓6と対向する位置に、
光電子増倍管4が設けられており、オゾン導入用
パイプ2から排出されるオゾンの流線5′と一酸
化窒素導入用パイプ3から排出される一酸化窒素
の流線5とが接触することにより発生される9000
〜30000Åのスペクトルを持つ近赤外線を検出す
る。
A typical conventional example of a chemiluminescence reaction chamber used in this analyzer is explained with reference to FIG. 1. 1 is a chemiluminescence reaction chamber made of stainless steel to block the incidence of light from the outside, and 2 is a chemiluminescence reaction chamber made of stainless steel to block the incidence of light from the outside. A pipe 3 introduces ozone into the chemiluminescence reaction chamber 1, and a pipe 3 similarly introduces a gas containing nitrogen monoxide to be measured into the chemiluminescence reaction chamber 1. The ends of these pipes 2 and 3 are bent inward so that ozone and nitrogen monoxide discharged from these pipes come into contact and mix. 6 is a glass window, and the chemiluminescence reaction chamber 1 has a glass window 7.
It is fixed via a fixing member such as a screw shown below. At a position facing this glass window 6,
A photomultiplier tube 4 is provided so that the streamline 5' of ozone discharged from the pipe 2 for introducing ozone and the streamline 5 of nitrogen monoxide discharged from the pipe 3 for introducing nitric oxide come into contact. 9000 generated by
Detects near-infrared light with a spectrum of ~30000Å.

この構成による化学発光反応室1においては、
オゾンと一酸化窒素との流線5と5′とが交差す
るタイプのものであるから、両者の接触確率が不
十分となり、化学発光分析法の特徴とするリニア
リテイが悪くなるということが実験上確認され
た。さらに具体的にいうと、化学発光反応室内を
常圧状態に保ち発光させた場合、一酸化窒素が0
〜500ppmの濃度領域においてはリニアリテイは
得られるが、500ppm以上の濃度領域においては
リニアリテイは劣化してしまう。
In the chemiluminescence reaction chamber 1 with this configuration,
Experiments have shown that since the streamlines 5 and 5' of ozone and nitric oxide intersect, the probability of contact between the two is insufficient and the linearity, which is a characteristic of chemiluminescence spectrometry, deteriorates. confirmed. More specifically, when the chemiluminescence reaction chamber is kept at normal pressure and emitted light, nitric oxide is 0.
Linearity is obtained in the concentration range of ~500 ppm, but linearity deteriorates in the concentration range of 500 ppm or more.

このような欠点に対処するため、従来はオゾン
と一酸化窒素との化学発光反応室への流速を落と
すと共に化学発光反応室の容積を大又は長くし、
受光面積の一層大きな光電子増倍管を用いていた
が、これによると分析計自体の容積が大となり、
装置のコンパクト化の時代の要請に逆行するもの
となり、また光電子増倍管が持つ寿命が本来的に
短かいので、これを取り換える必要があり、メン
テナンスに費用が嵩むという欠点があつた。
In order to deal with these drawbacks, conventional methods have been to reduce the flow rate of ozone and nitrogen monoxide into the chemiluminescence reaction chamber, increase the volume of the chemiluminescence reaction chamber, or increase the length of the chemiluminescence reaction chamber.
A photomultiplier tube with a larger light-receiving area was used, but this increased the volume of the analyzer itself.
This went against the demands of the times for more compact equipment, and since photomultiplier tubes have an inherently short lifespan, they had to be replaced, resulting in high maintenance costs.

一方、半導体光センサが出現しているが、この
センサは長寿命であり、かつ装置の小型化の要請
に対応できるが、受光面積が小さいため、リニア
リテイが一層悪くなり、実用上使用に耐えないも
のであつた。
On the other hand, semiconductor optical sensors have appeared, but although these sensors have a long life and can meet the demands for miniaturization of devices, the light receiving area is small, resulting in poor linearity, making them unsuitable for practical use. It was hot.

(ハ) 目的 本発明は、前記した従来技術の有する欠点を解
消するもので、半導体光センサの持つ欠点を除
き、その長所を生かした全く新規な化学発光反応
室を備える化学発光式分析計を提供することを目
的とする。
(c) Purpose The present invention eliminates the drawbacks of the prior art described above, and provides a chemiluminescence analyzer equipped with a completely new chemiluminescence reaction chamber that eliminates the drawbacks of semiconductor optical sensors and takes advantage of its advantages. The purpose is to provide.

(ニ) 構成 本発明は、化学発光反応室に一酸化窒素を含む
ガスを導入するパイプと、これを包囲するオゾン
導入管とにより2重管構造を形成し、オゾンの流
れにより一酸化窒素を含むガスの流れを層流とな
し、オゾンと一酸化窒素との混合、接触を理想的
なものとなし、かつオゾン導入管内で完全な発光
を行なわせ、これを確実にオゾン導入管排出端に
直角対面する半導体光センサにより検出すること
ができる。
(D) Structure The present invention forms a double pipe structure with a pipe for introducing a gas containing nitrogen monoxide into a chemiluminescence reaction chamber and an ozone introduction pipe surrounding the pipe, so that nitrogen monoxide is produced by the flow of ozone. The gas flow is laminar, the mixing and contact of ozone and nitrogen monoxide is ideal, and complete luminescence occurs within the ozone introduction tube, and this is ensured at the discharge end of the ozone introduction tube. It can be detected by semiconductor optical sensors facing each other at right angles.

(ホ) 実施例 第2図により、本発明の化学発光式分析計の実
施例を説明する。
(E) Example An example of the chemiluminescent analyzer of the present invention will be explained with reference to FIG.

同図において、1はステンレス製の化学発光反
応室であり、1′は化学発光反応室1内において
発光反応を終了した二酸化窒素と酸素とが排出さ
れる排出部である。2はオゾン導入用パイプで、
化学発光反応室1の壁面1aの中央部において直
角状に曲げられて化学発光反応室1内に挿入さ
れ、ガラス窓6の近くまで伸びている。3は測定
しようとする一酸化窒素を含むガスを導入するパ
イプで、オゾン導入用パイプ2の孔設部2′から
オゾン導入用パイプ2内に挿入され、2重管部を
形成する。一酸化窒素を包含するガスの導入用パ
イプ3の内径aは例えば0.5mmであり、パイプ3
を内包しガラス窓6の近くに達するオゾン導入用
パイプ2の内径bは例えば4mmとなつている。6
はガラス窓で、化学発光反応室1のフランジ5に
対しパツキン7を介し、不図示のねじなどの固定
部材により固定される。4は例えば10mm角の半導
体光センサで、オゾン導入用パイプ2の先端部
2″に対向する位置に配置される。オゾン導入用
パイプ2の先端部2″からガラス窓6の内面に至
る距離cは例えば5mmであり、ガラス窓6の内面
から一酸化窒素を含むガスを導入するパイプ3の
先端部3′に至る距離dは例えば40mmである。l1
はパイプ3から排出される一酸化窒素を含むガス
の流れを示し、その外側に位置するl2はパイプ2
から排出されるオゾンの流れを示す。
In the figure, 1 is a chemiluminescence reaction chamber made of stainless steel, and 1' is an exhaust section from which nitrogen dioxide and oxygen that have completed the luminescence reaction in the chemiluminescence reaction chamber 1 are discharged. 2 is a pipe for introducing ozone,
The wall 1a of the chemiluminescence reaction chamber 1 is bent at a right angle at the center thereof, inserted into the chemiluminescence reaction chamber 1, and extends close to the glass window 6. A pipe 3 introduces a gas containing nitrogen monoxide to be measured, and is inserted into the ozone introduction pipe 2 through the hole 2' of the ozone introduction pipe 2 to form a double pipe section. The inner diameter a of the pipe 3 for introducing gas containing nitrogen monoxide is, for example, 0.5 mm, and the pipe 3
The inner diameter b of the ozone introducing pipe 2 which contains the ozone and reaches near the glass window 6 is, for example, 4 mm. 6
is a glass window, which is fixed to the flange 5 of the chemiluminescence reaction chamber 1 via a packing 7 with a fixing member such as a screw (not shown). 4 is, for example, a 10 mm square semiconductor optical sensor, which is arranged at a position opposite to the tip 2'' of the ozone introduction pipe 2. The distance c from the tip 2'' of the ozone introduction pipe 2 to the inner surface of the glass window 6 is is, for example, 5 mm, and the distance d from the inner surface of the glass window 6 to the tip 3' of the pipe 3 into which the gas containing nitrogen monoxide is introduced is, for example, 40 mm. l 1
indicates the flow of gas containing nitric oxide discharged from pipe 3, and l 2 located outside it indicates pipe 2
This shows the flow of ozone emitted from the

この構成において、パイプ2から排出されるオ
ゾン3の流れl2はパイプ3から排出される一酸化
窒素を含むガスの流れl1の外側を流れ、これによ
り流れl1に理想的な層流を形成させる。この流れ
l1とl2、即ちガス中に含まれる一酸化窒素とオゾ
ンとがパイプ3の先端部3′からガラス窓に至る
までに十分に接触、混合され、化学反応が100%
行なわれ、ガラス窓6の内面にぶつかつた後に反
射され、排気部1′から排出されて行く。前記し
た化学反応が行なわれる反応領域はオゾン排出用
パイプ3の内径内に限定されているため、例えば
10mm角程度の小型の半導体光センサ4に対し十分
に受光され得る小さな発光光源に絞られた形の光
源となり、従つてこれを小型の半導体光センサ4
により完全に検出することができる。
In this configuration, the stream l 2 of ozone 3 exiting pipe 2 flows outside the stream l 1 of gas containing nitric oxide exiting pipe 3, thereby imparting ideal laminar flow to stream l 1. Let it form. this flow
l 1 and l 2 , that is, nitrogen monoxide and ozone contained in the gas, are sufficiently contacted and mixed from the tip 3' of the pipe 3 to the glass window, and the chemical reaction is 100%.
After hitting the inner surface of the glass window 6, it is reflected and exhausted from the exhaust section 1'. Since the reaction area where the chemical reaction described above takes place is limited to the inner diameter of the ozone discharge pipe 3, for example,
The light source is narrowed down to a small light emitting light source that can receive enough light for the small semiconductor photosensor 4 of about 10 mm square, and therefore this is used as the small semiconductor photosensor 4.
can be completely detected.

以上説明したように、2重管構造をなし、これ
により一酸化窒素とオゾンとの混合接触が理想的
に行なわれるため、オゾン濃度を低下することが
でき、換言すると大流量のオゾンを流すことがで
き、その結果、励起状態にあるNO2※がCO2と衝
突して生じるクエンチング効果を除去でき、測定
結果に対する二酸化炭素の干渉を従来のものに比
し半分にすることができる。
As explained above, the double-pipe structure allows for ideal mixing and contact between nitric oxide and ozone, making it possible to lower the ozone concentration, in other words, allowing a large flow of ozone to flow. As a result, the quenching effect that occurs when NO 2 * in an excited state collides with CO 2 can be removed, and the interference of carbon dioxide on measurement results can be halved compared to conventional methods.

本発明者等の実験によると、オゾンが毎分1.75
リツトルの流量で、一酸化窒素を含むガスが毎分
300c.c.の流量の場合に、リニアリテイが最も優れ
ていることが判明した。そして、この時の分析結
果に対する二酸化炭素の干渉は、10Vol.%の二酸
化炭素に対し1.8%であり、従来のそれが7%〜
8%であつたものに比し遥かに低く、測定精上無
視しうるものであつた。
According to experiments conducted by the inventors, ozone is absorbed at 1.75% per minute.
liter of gas containing nitric oxide per minute.
It was found that the linearity was the best at a flow rate of 300c.c. The interference of carbon dioxide in the analysis results at this time was 1.8% for 10Vol.% carbon dioxide, compared to the conventional interference of 7% to
This was much lower than 8%, and could be ignored in terms of measurement precision.

(ヘ) 効果 以上説明したように本発明によると、一酸化窒
素を含むガスの導入パイプの外側にオゾン導入パ
イプを設けて2重管構造とし、化学発光反応室の
ガラス窓の近くにオゾン導入パイプを延伸させ、
このオゾン導入パイプの前方直角面に半導体光セ
ンサを配置する構成としたから、一酸化窒素を含
むガスの流れがその外側を流れるオゾンの流れに
より層流に形成され、化学発光反応室のガラス面
に至るまでの間にオゾンと一酸化窒素との混合、
接触が完全に行なわれ、その際発生される発光量
を半導体光センサにより検出することができ、従
来のものでは得られなかつた500ppm以上の領域
においてもリニアリテイを得ることができると共
に、また両者の接触反応が理想的に行なわれるこ
とによりオゾン濃度が低下でき、従つて二酸化炭
素の干渉を従来のものよりも低下させることがで
きる。
(f) Effects As explained above, according to the present invention, an ozone introduction pipe is provided outside the introduction pipe for gas containing nitrogen monoxide to form a double pipe structure, and ozone is introduced near the glass window of the chemiluminescence reaction chamber. Stretch the pipe,
Since the semiconductor optical sensor is arranged at the right angle in front of this ozone introduction pipe, the flow of gas containing nitrogen monoxide is formed into a laminar flow by the flow of ozone flowing outside, and the glass surface of the chemiluminescence reaction chamber is The mixture of ozone and nitric oxide,
When the contact is complete, the amount of light emitted at that time can be detected by a semiconductor optical sensor, and it is possible to obtain linearity even in the region of 500 ppm or more, which was not possible with conventional methods, and also to improve the relationship between the two. By ideally carrying out the catalytic reaction, the ozone concentration can be lowered, and therefore the interference of carbon dioxide can be lowered than in the conventional case.

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

第1図は従来の化学発光式分析計の断面図、第
2図は本発明の化学発光式分析計の実施例の断面
図を示す。 図中、1は化学発光反応室、2はオゾン導入用
のパイプ、3は一酸化窒素を含むガス導入用パイ
プ、4は半導体光センサ、5はフランジ、6はガ
ラス窓、7はパツキン、l1は一酸化窒素を含むガ
スの流れ、l2はオゾンの流れを示す。
FIG. 1 is a sectional view of a conventional chemiluminescent analyzer, and FIG. 2 is a sectional view of an embodiment of the chemiluminescent analyzer of the present invention. In the figure, 1 is a chemiluminescence reaction chamber, 2 is a pipe for introducing ozone, 3 is a pipe for introducing gas containing nitrogen monoxide, 4 is a semiconductor optical sensor, 5 is a flange, 6 is a glass window, 7 is a packing, l 1 indicates the flow of gas containing nitric oxide, l 2 indicates the flow of ozone.

Claims (1)

【特許請求の範囲】 1 化学発光反応室の一方の側面から挿通された
一酸化窒素を含むガスを導入するガス導入管と、
この導入管の外側に挿通されたオゾン導入管と、
化学発光反応室の他方の側面に設けられたガラス
窓の外側でそのオゾン導入管に対面配設された半
導体光センサとを備え、このオゾン導入管を流れ
るオゾンの流れにより一酸化窒素を含むガスの流
れを層流となし、オゾン導入管内で発光を行なわ
せる化学発光式分析計。 2 前記したオゾン導入管の内径は4ミリ、前記
した一酸化窒素を含むガスを導入するガス導入管
の内径は0.5ミリ、前記したオゾン導入管の先端
部からガラス窓の内面までの距離が5ミリ、そし
て一酸化窒素を含むガスを導入するガス導入管の
先端部からガラス窓内面の距離が40ミリである特
許請求の範囲第1項記載の化学発光式分析計。
[Scope of Claims] 1. A gas introduction tube inserted from one side of the chemiluminescence reaction chamber and introducing a gas containing nitric oxide;
An ozone introduction pipe inserted outside this introduction pipe,
A semiconductor optical sensor is provided facing the ozone introduction tube outside the glass window provided on the other side of the chemiluminescence reaction chamber, and gas containing nitrogen monoxide is generated by the flow of ozone flowing through the ozone introduction tube. A chemiluminescence analyzer that generates light in the ozone introduction tube by making the flow a laminar flow. 2 The inner diameter of the ozone introduction tube described above is 4 mm, the inner diameter of the gas introduction tube that introduces the gas containing nitrogen monoxide is 0.5 mm, and the distance from the tip of the ozone introduction tube to the inner surface of the glass window is 5 mm. 2. The chemiluminescent analyzer according to claim 1, wherein the distance from the tip of the gas introduction tube through which the gas containing nitrogen monoxide is introduced to the inner surface of the glass window is 40 mm.
JP22645883A 1983-11-30 1983-11-30 Chemiluminescence analyzer Granted JPS60119445A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP22645883A JPS60119445A (en) 1983-11-30 1983-11-30 Chemiluminescence analyzer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22645883A JPS60119445A (en) 1983-11-30 1983-11-30 Chemiluminescence analyzer

Publications (2)

Publication Number Publication Date
JPS60119445A JPS60119445A (en) 1985-06-26
JPH0452892B2 true JPH0452892B2 (en) 1992-08-25

Family

ID=16845407

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22645883A Granted JPS60119445A (en) 1983-11-30 1983-11-30 Chemiluminescence analyzer

Country Status (1)

Country Link
JP (1) JPS60119445A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2292596A2 (en) 1997-02-12 2011-03-09 Japan Tobacco, Inc. CETP activity inhibitor

Cited By (1)

* Cited by examiner, † Cited by third party
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EP2292596A2 (en) 1997-02-12 2011-03-09 Japan Tobacco, Inc. CETP activity inhibitor

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