JPH09178653A - Measuring method for ozone concentration - Google Patents

Measuring method for ozone concentration

Info

Publication number
JPH09178653A
JPH09178653A JP35079295A JP35079295A JPH09178653A JP H09178653 A JPH09178653 A JP H09178653A JP 35079295 A JP35079295 A JP 35079295A JP 35079295 A JP35079295 A JP 35079295A JP H09178653 A JPH09178653 A JP H09178653A
Authority
JP
Japan
Prior art keywords
gas
room
reference gas
ozone concentration
sample
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.)
Pending
Application number
JP35079295A
Other languages
Japanese (ja)
Inventor
Hironori Shimizu
水 博 則 清
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.)
Ebara Jitsugyo Co Ltd
Original Assignee
Ebara Jitsugyo Co Ltd
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 Ebara Jitsugyo Co Ltd filed Critical Ebara Jitsugyo Co Ltd
Priority to JP35079295A priority Critical patent/JPH09178653A/en
Publication of JPH09178653A publication Critical patent/JPH09178653A/en
Pending legal-status Critical Current

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  • Sampling And Sample Adjustment (AREA)
  • Optical Measuring Cells (AREA)
  • Investigating Or Analysing Materials By Optical Means (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a measuring method in which an ozone concentration inside a room can be measured without being affected by an oxidant taken into the room from the open air by a method wherein the open air is sampled as a reference gas. SOLUTION: A reference gas is introduced into a measuring cell 9 via a reference-gas pipe passage 2 from a reference-gas sampling port 1, a valve 8 is changed over, and a sample gas is introduced into the measuring cell 9 from a sample-gas pipe 6. The reference gas and the sample gas which are passed through the cell 9 are discharged from a discharge pipe 13 by a pump 15. Then, the inside of the cell 9 is irradiated with a light source 10, transmitted light is received by a detector 11, an output from the detector 11 is processed by a computing part 12, and a measurement is performed in the same manner as in conventional cases. At this time, the sampling port 1 is made to protrude to the outside of a room, and the open air is sampled as the reference gas as it is. As a result, a false report and a malfunction due to the influence of a photochemical oxidant which is taken into the room from the open air are eliminated, and an ozone concentration inside the room can be measured.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、室内のオゾン濃度の
測定方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for measuring ozone concentration in a room.

【0002】[0002]

【従来の技術】オゾンの有する優れた酸化力、殺菌力、
脱臭力は上下水道の処理等に利用されている反面、その
濃度によって人体、環境、機器に悪影響を及ぼす。従っ
てオゾンを利用した処理プラントにおいては、オゾン発
生器室等のオゾンガスがリ−クする可能性のある室(本
願において、室)のオゾン濃度を常に監視することが必
要となる。
2. Description of the Related Art Ozone has excellent oxidizing power, sterilizing power,
Although the deodorizing power is used for the treatment of water and sewage, its concentration adversely affects the human body, environment and equipment. Therefore, in a processing plant using ozone, it is necessary to constantly monitor the ozone concentration in a room (in the present application, the room) where ozone gas may leak such as an ozone generator room.

【0003】従来より吸光光度測定により室内のオゾン
ガスの濃度測定を行なう場合、基準ガス生成器によって
生成された基準ガス(オゾンガスを含まないガス=ゼロ
ガス)を測定セルに流し、該測定セル内に紫外線等の光
線を照射してその透過量を測定することにより基準値を
求める。次に、測定の対象となる室内より採取したガス
(試料ガス)をそのまま測定セルに流し、上記同様紫外
線の透過量を測定する。こうして得られる両出力の関係
(ランバ−ト・ベ−ルの法則)から濃度を測定する。
Conventionally, when the concentration of ozone gas in a room is measured by absorptiometry, a reference gas (gas not containing ozone gas = zero gas) generated by a reference gas generator is flown into a measurement cell, and ultraviolet rays are introduced into the measurement cell. A reference value is obtained by irradiating a light beam such as the above and measuring the amount of transmission. Next, the gas (sample gas) sampled from the chamber to be measured is flown into the measurement cell as it is, and the amount of transmitted ultraviolet rays is measured as described above. The concentration is measured from the relationship between the two outputs thus obtained (Lambert-Beer's law).

【0004】上記方法により、室内に設置されるオゾン
発生器や反応槽、配管等からのオゾンガスの漏れを監視
し、ガス濃度が一定以上(一般的には0.06ppmか
ら0.1ppm程度)となった場合は警報を発したり、
処理プラントが停止したりする。
By the above method, leakage of ozone gas from the ozone generator, reaction tank, piping, etc. installed in the room is monitored, and the gas concentration is above a certain level (generally 0.06 to 0.1 ppm). When it becomes, an alarm is issued,
The processing plant shuts down.

【0005】ところで、我が国の大気汚染状況は厳しい
状況にあり、特に光化学オキシダントによる汚染は深刻
である。光化学オキシダントは、工場や自動車から排出
される窒素酸化物や炭化水素等を主体とする一次汚染物
質が、太陽光線の照射を受けて光化学反応をおこすこと
により二次的に生成される強い酸化力を持った物質であ
り、その主成分はオゾンである。
By the way, the air pollution situation in Japan is severe, and the pollution by photochemical oxidants is particularly serious. A photochemical oxidant is a strong oxidative power that is secondarily generated by the photochemical reaction of primary pollutants mainly composed of nitrogen oxides and hydrocarbons emitted from factories and automobiles when they are exposed to sunlight. It is a substance with a chemical substance, and its main component is ozone.

【0006】光化学オキシダントは光化学スモッグの原
因となり、高濃度においては粘膜への刺激や呼吸器への
影響があるため、「1時間値が0.06ppm以下であ
ること」という環境基準が設定されており、1時間値が
0.12ppm以上であり、気象条件からみてその状態
が継続すると認められるときは、都道府県知事等が注意
報を発令する。平成6年の光化学オキシダントの注意報
発令延日数は175日に達しており、特に首都圏地域及
び近畿圏地域に注意報の発令が集中している(図1)。
Photochemical oxidants cause photochemical smog, and at high concentrations, they cause irritation to mucous membranes and affect respiratory organs. Therefore, the environmental standard "1 hour value is 0.06 ppm or less" has been set. If the hourly value is 0.12 ppm or more and it is recognized that the condition will continue due to weather conditions, the prefectural governor, etc. will issue a warning. The number of days for issuing warnings for photochemical oxidants in 1994 has reached 175 days, and warnings are particularly concentrated in the Tokyo metropolitan area and Kinki area (Fig. 1).

【0007】上記の環境の下で室内の換気は、通常、換
気口等をとおして大気を直接室内に取り入れることによ
り行なわれるため、大気中に含まれる光化学オキシダン
トも共に室内に取り込まれることとなる。従って、光化
学オキシダントの主成分であるオゾンも取り込まれるこ
ととなる。
Under the above-mentioned environment, indoor ventilation is usually carried out by directly introducing the air into the room through a ventilation port or the like, so that the photochemical oxidant contained in the atmosphere is also taken into the room. . Therefore, ozone, which is the main component of the photochemical oxidant, is also taken in.

【0008】図2をみると、大気中のオゾン濃度の変化
と測定室内におけるオゾン濃度とは相関関係があること
がわかる。
It can be seen from FIG. 2 that there is a correlation between the change in the ozone concentration in the atmosphere and the ozone concentration in the measuring chamber.

【0009】[0009]

【発明が解決しようとする課題】従来方法によりオゾン
濃度測定を行なう場合、基準ガスが基準ガス生成器をと
おしてほぼ完全にゼロガス化されるが、室内には、換気
により外気に発生する光化学オキシダントが直接取り込
まれるため、基準ガスと室内のガスリ−クがない状態の
空気のガス濃度との間にズレが生じる。
When the ozone concentration is measured by the conventional method, the reference gas is almost completely converted to zero gas through the reference gas generator, but inside the room, the photochemical oxidant generated in the outside air by ventilation is generated. Is directly taken in, there is a gap between the reference gas and the gas concentration of air in the absence of gas leak in the room.

【0010】従って、室内に設置されたオゾン濃度測定
装置が、換気により室内に取り込まれたオキシダントに
含まれるオゾンを検出し、オゾン発生器等からオゾンガ
スが漏れていないにもかかわらず警報を発したり、処理
プラントが停止する等の不都合が生じていた。本発明は
上記欠点を除去するために為されたものである。
Therefore, the ozone concentration measuring device installed in the room detects ozone contained in the oxidant taken into the room by ventilation, and issues an alarm even if ozone gas is not leaking from the ozone generator or the like. However, there were inconveniences such as the stop of the processing plant. The present invention has been made to eliminate the above drawbacks.

【0011】[0011]

【課題を解決するための手段】室内のオゾンガス濃度の
測定装置において、大気を基準ガスとして採取すること
によりオゾン濃度を測定する。本発明は以上を特徴とし
てオゾンガス濃度を測定する方法である。
In an indoor ozone gas concentration measuring device, the ozone concentration is measured by sampling the atmosphere as a reference gas. The present invention is a method for measuring ozone gas concentration, which is characterized by the above.

【0012】大気を基準ガスとして取り込むため、外気
から室内に取り込まれた光化学オキシダントの影響を受
けて誤報、誤作動等することなく、室内のオゾン濃度を
測定することが出来る。
Since the atmospheric air is taken in as the reference gas, the ozone concentration in the room can be measured without being affected by the photochemical oxidant taken in from the outside air to cause false alarms or malfunctions.

【0013】[0013]

【発明の実施の形態】以下、本発明の実施の形態につい
て説明する。室内に、オゾンガス濃度測定装置を設置す
る。たとえば イ)基準ガスと試料ガスが流される測定セル(9)と、 ロ)始端に基準ガス採取口(1)を有し基準ガスを測定
セル(9)に導く基準ガス管路(2)及び試料ガスを測
定セル(9)に導くための試料ガス管(6)を設け、 ハ)測定セル(9)に基準ガスと試料ガスを切り替えて
流すことが出来るバルブ(8)を設け、 ニ)測定セル(9)を通過した基準ガスまたは試料ガス
の排出管(13)を設ける。排出管(13)には基準ガ
ス及び試料ガスを流すためのポンプ(15)が設けられ
ている。 ホ)測定セル(9)内にを照射する光源(10)と、測
定セル(9)内を通過した光線を受けるディテクタ(1
1)を設け、 ヘ)ディテクタ(11)からの出力を処理するための演
算部(12)を設ける。尚、排出管(13)には必要に
応じて分解器(14)を設置する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below. An ozone gas concentration measuring device is installed in the room. For example, a) a measurement cell (9) in which a reference gas and a sample gas are flown, and (b) a reference gas pipe (2) having a reference gas sampling port (1) at the beginning and guiding the reference gas to the measurement cell (9) and A sample gas pipe (6) for guiding the sample gas to the measurement cell (9) is provided, and (c) a valve (8) capable of selectively flowing the reference gas and the sample gas is provided in the measurement cell (9). An exhaust pipe (13) for the reference gas or sample gas that has passed through the measurement cell (9) is provided. The discharge pipe (13) is provided with a pump (15) for flowing the reference gas and the sample gas. (E) A light source (10) for irradiating the inside of the measuring cell (9) and a detector (1) for receiving a light beam that has passed through the inside of the measuring cell (9).
1) is provided, and f) an arithmetic unit (12) for processing the output from the detector (11) is provided. A disassembler (14) is installed in the discharge pipe (13) as required.

【0014】以上を基本的な構成とするオゾン濃度測定
装置を設置する。このとき、基準ガス管の基準ガス採取
口(1)を室外に出す等により、大気をそのまま基準ガ
スとして採取出来るようにする。従って基準ガス生成装
置(7)は不要となる。測定は従来の方法と同様に行な
う。
An ozone concentration measuring device having the above basic structure is installed. At this time, the reference gas sampling port (1) of the reference gas pipe is taken out of the room so that the atmosphere can be directly collected as the reference gas. Therefore, the reference gas generator (7) is unnecessary. The measurement is performed in the same manner as the conventional method.

【0015】以下、実験デ−タをもとに基準ガスの採取
について述べる。通常換気を行なった場合、外気の光化
学オキシダント濃度とその影響を受けた室内の濃度に
は、既述の通り相関関係があるものの(図2)、換気の
回数や換気扇の使用等の諸条件によって濃度差に変動が
生じる(図3、図4)。
The sampling of the reference gas will be described below based on the experimental data. In the case of normal ventilation, the photochemical oxidant concentration in the outside air and the concentration in the room affected by it have a correlation as described above (Fig. 2), but depending on various conditions such as the frequency of ventilation and the use of a ventilation fan. The density difference fluctuates (FIGS. 3 and 4).

【0016】また、外気を採取する際に、基準ガス採取
管の基準ガス取り入れ口をただ室外に出すだけでは、風
向きの影響等により前記濃度差の変動の幅が大きくなる
傾向にある。
Further, when the outside air is sampled, if the reference gas intake port of the reference gas sampling pipe is simply taken out of the room, the fluctuation range of the concentration difference tends to become large due to the influence of the wind direction and the like.

【0017】従って、大気中の光化学オキシダント濃度
とその影響を受けた室内の濃度の変動を安定させるた
め、 イ)基準ガス採取口(1)は、換気扇等の換気装置
(4)の外気流入口付近あるいは換気装置のダクト
(5)内等のように風向きが一定となる場所に配設する
のが適当である。こうすることで、基準ガスの濃度を、
基準ガスとして最適なオキシダントの影響を受けた室内
の濃度に近付けることが可能である。 ロ)前記測定結果(図3、図4)を参考に換気回数を選
択することによって、測定する環境を安定させる。以上
の条件を考慮することによって、本発明をより有効に実
施することができる。
Therefore, in order to stabilize the fluctuation of the photochemical oxidant concentration in the atmosphere and the concentration in the room affected by it, a) the reference gas sampling port (1) is the outside air inlet of the ventilation device (4) such as a ventilation fan. It is suitable to dispose in the vicinity or in a place where the wind direction is constant, such as in the duct (5) of the ventilation device. By doing this, the concentration of the reference gas
It is possible to approach the indoor concentration affected by the oxidant, which is optimum as the reference gas. B) The measurement environment is stabilized by selecting the ventilation frequency with reference to the measurement results (FIGS. 3 and 4). The present invention can be more effectively implemented by considering the above conditions.

【0018】[0018]

【発明の効果】外気から室内に取り込まれたオキシダン
トの影響を受けることなく、室内のオゾン濃度の測定及
びオゾンリ−クの監視をすることができ、室内に取り込
まれたオキシダントに含まれるオゾンを検出することに
よる誤報、誤作動等を防ぐことが出来る。
Industrial Applicability The ozone concentration in the room and the ozone leak can be monitored without being affected by the oxidant taken in from the outside air, and the ozone contained in the oxidant taken in the room can be detected. It is possible to prevent false alarms, malfunctions, etc.

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

【図1】 平成6年の各都道府県の注意報等発令延日数[Fig. 1] Number of postponement days of issuance of warnings, etc. for each prefecture in 1994

【図2】 オゾン発生器室オゾン濃度と大気オキシダン
ト濃度の関係
[Figure 2] Relationship between ozone concentration in ozone generator room and atmospheric oxidant concentration

【図3】 1時間あたり3回換気を行なった場合の測定
室内オゾンと大気オキシダントの濃度差
[Fig. 3] Concentration difference between ozone and atmospheric oxidant in the measurement room when ventilation is performed three times per hour

【図4】 1時間あたり換気回数による濃度差[Fig. 4] Concentration difference due to ventilation frequency per hour

【図5】 従来のオゾンガス濃度測定装置FIG. 5: Conventional ozone gas concentration measuring device

【図6】 本発明の実施例FIG. 6 shows an embodiment of the present invention.

【図7】 基準ガス採取口を外気流入口付近に配設した
本発明の実施例
FIG. 7 is an embodiment of the present invention in which a reference gas sampling port is arranged near the outside airflow inlet.

【図8】 基準ガス採取口をダクト内に配設した本発明
の実施例
FIG. 8 is an embodiment of the present invention in which a reference gas sampling port is provided in a duct.

【符号の説明】[Explanation of symbols]

1 基準ガス採取口 2 基準ガス管路 3 オゾン濃度測定装置 4 換気装置 5 ダクト 6 試料ガス管 7 基準ガス生成装置 8 バルブ 9 測定セル 10 光源 11 ディテクタ 12 演算部 13 排出管 14 分解器 15 ポンプ 1 Reference Gas Sampling Port 2 Reference Gas Pipeline 3 Ozone Concentration Measuring Device 4 Ventilation Device 5 Duct 6 Sample Gas Pipe 7 Reference Gas Generation Device 8 Valve 9 Measuring Cell 10 Light Source 11 Detector 12 Computational Section 13 Discharge Pipe 14 Decomposer 15 Pump

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】室内のオゾン濃度の測定において、大気を
基準ガスとして採取することを特徴とするオゾン濃度測
定方法。
1. A method for measuring ozone concentration, characterized in that in the measurement of ozone concentration in a room, air is sampled as a reference gas.
【請求項2】基準ガスと試料ガスが流される測定セル
と、始端に基準ガス採取口を有し基準ガスを該測定セル
に導く基準ガス管路及び試料ガスを該測定セルに導くた
めの試料ガス管と、該測定セルに基準ガスと試料ガスを
切り替えて流すことが出来るバルブと、該測定セルに連
通し且つポンプを有する基準ガスまたは試料ガスの排出
管と、該測定セル内に光線を照射する光源と、該測定セ
ル内を通過した光線を受けるディテクタと、該ディテク
タからの出力を処理するための演算部を設けたオゾン濃
度測定装置において、 測定する室へ換気装置を設け、前記基準ガス採取口を室
内の換気装置の外気流入口付近に配設した請求項1のオ
ゾン濃度測定装置。
2. A measurement cell in which a reference gas and a sample gas are caused to flow, a reference gas pipe having a reference gas sampling port at its starting end for guiding the reference gas to the measurement cell, and a sample for guiding the sample gas to the measurement cell. A gas pipe, a valve capable of switching a reference gas and a sample gas to flow in the measurement cell, a reference gas or sample gas discharge pipe having a pump and communicating with the measurement cell, and a light beam in the measurement cell. In an ozone concentration measuring device provided with a light source for irradiating, a detector for receiving a light beam that has passed through the measuring cell, and an arithmetic unit for processing the output from the detector, a ventilation device is provided for the chamber to be measured, The ozone concentration measuring device according to claim 1, wherein the gas sampling port is arranged near an outside airflow inlet of the ventilation device in the room.
【請求項3】測定する室へ換気装置を設け、基準ガス採
取口を換気装置のダクト内に配設した請求項2のオゾン
濃度測定装置。
3. The ozone concentration measuring device according to claim 2, wherein a ventilation device is provided in the chamber for measurement, and the reference gas sampling port is provided in the duct of the ventilation device.
JP35079295A 1995-12-26 1995-12-26 Measuring method for ozone concentration Pending JPH09178653A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP35079295A JPH09178653A (en) 1995-12-26 1995-12-26 Measuring method for ozone concentration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP35079295A JPH09178653A (en) 1995-12-26 1995-12-26 Measuring method for ozone concentration

Publications (1)

Publication Number Publication Date
JPH09178653A true JPH09178653A (en) 1997-07-11

Family

ID=18412907

Family Applications (1)

Application Number Title Priority Date Filing Date
JP35079295A Pending JPH09178653A (en) 1995-12-26 1995-12-26 Measuring method for ozone concentration

Country Status (1)

Country Link
JP (1) JPH09178653A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012013573A (en) * 2010-07-01 2012-01-19 Ibaraki Univ Ozone concentration meter and ozone concentration monitoring kit with the ozone concentration meter
CN104266974A (en) * 2014-10-21 2015-01-07 赵怀军 Forced airflow type open air chamber

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012013573A (en) * 2010-07-01 2012-01-19 Ibaraki Univ Ozone concentration meter and ozone concentration monitoring kit with the ozone concentration meter
CN104266974A (en) * 2014-10-21 2015-01-07 赵怀军 Forced airflow type open air chamber

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