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JPH0233964B2 - - Google Patents
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JPH0233964B2 - - Google Patents

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Publication number
JPH0233964B2
JPH0233964B2 JP57042333A JP4233382A JPH0233964B2 JP H0233964 B2 JPH0233964 B2 JP H0233964B2 JP 57042333 A JP57042333 A JP 57042333A JP 4233382 A JP4233382 A JP 4233382A JP H0233964 B2 JPH0233964 B2 JP H0233964B2
Authority
JP
Japan
Prior art keywords
dust
measured
ray
flow path
detector
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 - Lifetime
Application number
JP57042333A
Other languages
Japanese (ja)
Other versions
JPS58160806A (en
Inventor
Someyoshi Arai
Ryoichi Ishikawa
Masaki Mori
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.)
DKK TOA Corp
Original Assignee
DKK 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 DKK Corp filed Critical DKK Corp
Priority to JP4233382A priority Critical patent/JPS58160806A/en
Publication of JPS58160806A publication Critical patent/JPS58160806A/en
Publication of JPH0233964B2 publication Critical patent/JPH0233964B2/ja
Granted legal-status Critical Current

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Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N15/00Investigating characteristics of particles; Investigating permeability, pore-volume or surface-area of porous materials
    • G01N15/06Investigating concentration of particle suspensions
    • G01N15/0606Investigating concentration of particle suspensions by collecting particles on a support
    • G01N15/0618Investigating concentration of particle suspensions by collecting particles on a support of the filter type

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  • Chemical & Material Sciences (AREA)
  • Dispersion Chemistry (AREA)
  • Physics & Mathematics (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)
  • Length-Measuring Devices Using Wave Or Particle Radiation (AREA)
  • Analysing Materials By The Use Of Radiation (AREA)

Description

【発明の詳細な説明】 本発明はβ線透過式ダスト計に関する。[Detailed description of the invention] The present invention relates to a β-ray transmission type dust meter.

従来、β線を使用して大気中のダスト濃度を測
定する方法として、テープ状の紙で大気を過
して紙表面に大気中のダストを捕集し、この捕
集ダストによる透過β線の減衰の度合を測定し、
これからダスト濃度を求める方法がある。即ち、
この方法は透過β線強度と捕集ダストの厚さとの
間に次式(1)の関係が成立することを応用するもの
である。
Conventionally, the method of measuring the dust concentration in the atmosphere using β-rays is to pass through the atmosphere with a tape-shaped paper and collect the dust in the atmosphere on the surface of the paper. Measure the degree of attenuation,
There is a way to calculate the dust concentration from this. That is,
This method applies the fact that the following equation (1) holds between the transmitted β-ray intensity and the thickness of the collected dust.

I=I0exp(−μX) ………(1) ここで I:紙及びダストを透過したβ線強度 I0:紙のみを透過したβ線強度 μ:質量吸収係数(cm2/g) X:ダスト量(g/cm2) 更に、大気中のダスト濃度は(2)式により現わさ
れる。
I = I 0 exp (-μX) ...... (1) where I: β-ray intensity transmitted through paper and dust I 0 : β-ray intensity transmitted only through paper μ: Mass absorption coefficient (cm 2 /g) X: Dust amount (g/cm 2 ) Furthermore, the dust concentration in the atmosphere is expressed by equation (2).

C=A/μQtlnI0/I ………(2) ここで A:捕集面積(cm2) Q:通過流量(cm3/min) t:捕集時間(min) C:ダスト濃度(g/cm2) よつて、ダスト捕集前後の透過β線強度I0、I
を実測することにより、(2)式から大気中のダスト
濃度が求められるもので、この原理に基づくダス
ト計としては、従来第1図及び第2図に示すもの
がある。
C=A/μQtlnI 0 /I (2) where A: Collection area (cm 2 ) Q: Passing flow rate (cm 3 /min) t: Collection time (min) C: Dust concentration (g/ cm 2 ) Therefore, the transmitted β-ray intensity I 0 and I before and after dust collection
By actually measuring , the dust concentration in the atmosphere can be determined from equation (2). Conventional dust meters based on this principle are shown in FIGS. 1 and 2.

第1図のダスト計の場合には、紙aはロール
状紙bから繰り出され、過部cを通つて測定
部dに至り、ここでβ線源eから放射されるβ線
により紙が照射され、その透過β線強度I0がβ
線検出器fで測定され記憶される。次いで紙a
が巻きもどされて前記β線が照射されて透過β線
強度I0が測定された紙の部分が過部cに装着
される。その後、吸引ポンプが作動し、大気が吸
引管g内を下方向(図中矢印P方向)に吸引さ
れ、これにより大気中のダストが紙aによつて
別される。次いで、紙は再び繰り出され、
過部分が前記測定部dに移動せしめられた後、
紙及び過されて沈着したダスト層を透過したβ
線強度Iが測定され、このようにして求めたI0
びIから(2)式を用いてダスト濃度Cが算出される
ものである。なお、hはピンチローラ、iはキヤ
プスタン、jは巻き取りロールである。
In the case of the dust meter shown in Fig. 1, paper a is unwound from a roll of paper b, passes through a passage c, and reaches a measurement section d, where the paper is irradiated with β-rays emitted from a β-ray source e. and its transmitted β-ray intensity I 0 is β
It is measured by a line detector f and stored. Then paper a
The part of the paper that was rewound and irradiated with the β-rays and the transmitted β-ray intensity I 0 was measured is attached to the upper part c. Thereafter, the suction pump is activated, and atmospheric air is sucked downward (in the direction of arrow P in the figure) through the suction tube g, whereby dust in the atmosphere is separated by the paper a. The paper is then unrolled again and
After the excess portion is moved to the measurement part d,
β transmitted through paper and filtered and deposited dust layer
The line intensity I is measured, and the dust concentration C is calculated from I 0 and I obtained in this way using equation (2). In addition, h is a pinch roller, i is a capstan, and j is a winding roll.

第2図のダスト計の場合には、ロール状紙b
から繰り出された紙aは、まず測定部dにおい
て紙aの透過β線強度I0が測定された後、過
部cに送られ、ここで、大気が過される。次い
で、測定部dは吸引管gの軸線を中心として180
度回転され、図中2点鎖線で示す位置に測定部d
が移動せしめられると共に、紙aも移動し、鎖
線で示す位置において紙a及びダスト層を透過
したβ線強度Iが測定され、このようにして求め
たI0及びIから(2)式を用いてダスト濃度Cが算出
されるものである。
In the case of the dust meter shown in Figure 2, roll paper b
The paper a fed out from the measuring section d first measures the transmitted β-ray intensity I 0 of the paper a, and then is sent to the transfer section c, where the atmosphere is passed through. Next, the measurement part d is 180 degrees centering on the axis of the suction tube g.
The measuring part d is rotated by
is moved, and paper a is also moved, and the β-ray intensity I transmitted through paper a and the dust layer is measured at the position indicated by the chain line. Using equation (2) from I 0 and I obtained in this way, The dust concentration C is calculated using the following steps.

上記両ダスト計においては、測定部d及び過
部cに紙aの同一部分(過部分)を再現性良
く移動させることがダスト量を精度良く測定する
ための必要条件であるが、これは機構上なかなか
困難なことで、紙の移動の際に生じる上記各測
定位置及び吸引位置間のずれが直接測定誤差の原
因になる問題がある。
In both of the above-mentioned dust meters, moving the same part (over part) of paper a to measuring part d and over part c with good reproducibility is a necessary condition for accurately measuring the amount of dust. On the other hand, it is quite difficult to do so, and there is a problem in that the deviation between the above-mentioned measurement positions and the suction position that occurs when the paper is moved directly causes measurement errors.

上記問題を解決するものとして第3図に示すダ
スト計が提案されている(Friegeke社製)。この
ダスト計による場合には、大気はポンンプkによ
り吸引されて吸引管gに流入し、紙aによりダ
ストが別された後、β線照射路lを通り抜け更
に排出管mを通つて系外に排出される。このよう
にして別されて紙a上面に沈着したダストn
は、照射路の下部に装着されたβ線源の放射する
β線が照射され、その透過β線強度Iが紙上方
に配設された検出器fにより検出されるが、前記
ポンプkを作動させる前に予め紙aのみの場合
の透過β線強度I0を測定しておけば、ダスト濃度
は前記I0及びIから算出でき、しかもこの場合に
はI0、Iの測定における紙の移動がないので、
前2者のダスト計のように、紙の移動により生
じる紙の測定位置のずれに起因する測定誤差の
発生は考えられない。しかし、このダスト計の場
合には、大気は照射路lの側方からほぼ紙aに
平行に照射路lに供給され、紙aで過される
ため、ダストnが紙a上に不均一に沈着し易
い。このため、測定精度が低下す問題がある上、
大気が照射路lを通つて外部に排出される構造と
なつているため、照射路が微細なダストにより汚
れ易い。このため、この汚れを定期的に清掃する
必要があるが、これは繁雑なもので、しかも清掃
は構造上簡単に行ない難いものである。
A dust meter shown in FIG. 3 has been proposed to solve the above problem (manufactured by Friegeke). In the case of this dust meter, atmospheric air is sucked by a pump k and flows into a suction pipe g, and after the dust is separated by a paper a, it passes through a β-ray irradiation path l and then exits the system through a discharge pipe m. be discharged. Dust n separated in this way and deposited on the top surface of paper a
is irradiated with β-rays emitted by a β-ray source installed at the bottom of the irradiation path, and the transmitted β-ray intensity I is detected by a detector f arranged above the paper. If the transmitted β-ray intensity I 0 in the case of only paper a is measured beforehand, the dust concentration can be calculated from the above I 0 and I, and in this case, the movement of the paper in the measurement of I 0 and I Since there is no
Unlike the former two dust meters, it is unlikely that a measurement error will occur due to a shift in the measurement position of the paper caused by movement of the paper. However, in the case of this dust meter, the air is supplied to the irradiation path 1 from the side of the irradiation path 1 almost parallel to the paper a, and passes through the paper a, so the dust n is distributed non-uniformly on the paper a. Easily deposited. For this reason, there is a problem that measurement accuracy decreases, and
Since the structure is such that the atmosphere is exhausted to the outside through the irradiation path 1, the irradiation path is easily contaminated by fine dust. Therefore, it is necessary to periodically clean this dirt, but this is a complicated process, and furthermore, cleaning is difficult to perform simply due to the structure.

本発明は、上記事情を改善するためになされた
もので、β線源と、前記β線源から放射されるβ
線の照射路と、前記照射路に供給される材と、
前記材を透過するβ線量を検出する検出器と、
前記検出器の検出する信号を増幅して出力する増
幅部と、前記材と交差する被測程気体流路とか
らなり、前記材で被測定気体流路内を流れる被
測定気体を過して被測定気体中の浮遊粉塵を捕
集すると共に、この捕集した粉塵による材透過
β線の減衰量を前記検出器で検出し、この検出信
号を増幅部で増幅して出力することにより被測定
気体中の浮遊粉塵量を決定するダスト計におい
て、前記材と被測定気体流路との交差部にβ線
照射路を被測定気体流路と70度以下の角度で交差
させて連結すると共に、β線照射路を被測定気体
流路との交差部においてβ線透過性薄膜で閉塞し
てなるダスト計を提供する。
The present invention was made to improve the above situation, and includes a β-ray source and a β-ray source emitted from the β-ray source.
a line irradiation path; a material supplied to the irradiation path;
a detector that detects the amount of β-rays that passes through the material;
It consists of an amplification section that amplifies and outputs the signal detected by the detector, and a gas flow path to be measured that intersects the material, and the gas flow path is passed through the gas flow path through the material. At the same time as collecting floating dust in the gas to be measured, the detector detects the amount of attenuation of β-rays passing through the material due to the collected dust, and this detection signal is amplified by the amplifier and output. In a dust meter that determines the amount of suspended dust in a gas, a β-ray irradiation path is connected to the intersection of the material and the gas flow path to be measured by intersecting the gas flow path to be measured at an angle of 70 degrees or less, A dust meter is provided in which a β-ray irradiation path is closed with a β-ray permeable thin film at the intersection with a gas flow path to be measured.

本発明においては、被測定気体流路とβ線照射
路との交叉角を70度以下に形成したので、気体流
路と材面とのなす角度及びβ線照射路と材面
とのなす角度がいずれも直角により近くなり、こ
れによつて材面におけるダスト沈着層が材面
に対して均一に形成されると共に、ダスト沈着層
にβ線が直角に近い角度で照射され、このため透
過β線強度Iが正確に沈着量に対応するものとな
り、測定精度が向上したものである。
In the present invention, since the intersection angle between the gas flow path to be measured and the β-ray irradiation path is 70 degrees or less, the angle between the gas flow path and the material surface and the angle between the β-ray irradiation path and the material surface are are closer to the right angle, and as a result, the dust deposited layer on the material surface is formed uniformly on the material surface, and the dust deposited layer is irradiated with the β rays at an angle close to the right angle, so that the transmitted β The linear intensity I corresponds accurately to the amount of deposition, and the measurement accuracy is improved.

即ち、気体中のダストを材によつて捕集する
場合、材面に対して気体をできるだけ直角に近
い角度で流すことが材上にダストを均一に沈着
させる点で望ましく、材面に対する気体流路の
角度が小さくなると材周縁部の一部にダストが
多く沈着し、ダスト分布にかたよりが生じる。特
に、気体の流速が層流域を超えて乱流域に入る
と、このようなかたよりが顕著に生じる。そし
て、ダストの沈着量分布に上述したようなかたよ
りが生じた場合、β線透過式のダスト計では実際
に沈着したダスト量より少ない値が検出されてし
まう。
In other words, when collecting dust in a gas using a material, it is desirable to flow the gas at an angle as close to perpendicular to the surface of the material as possible in order to deposit the dust uniformly on the material. When the path angle becomes smaller, more dust is deposited on a part of the periphery of the material, causing a shift in dust distribution. Particularly, when the gas flow velocity exceeds the laminar region and enters the turbulent region, such a shift becomes noticeable. If the above-mentioned deviation occurs in the distribution of the amount of dust deposited, the β-ray transmission type dust meter will detect a value smaller than the amount of dust actually deposited.

これに対し、本発明においては、気体流路とβ
線照射路との交叉角θを70度以下に形成したこと
により、材面に対する気体流路の角度を大きく
して直角により近くすることができ、このため
材面にダストを均一に捕集し、ダスト濃度を精度
良く測定することが可能になつたものである。
On the other hand, in the present invention, the gas flow path and β
By forming the intersecting angle θ with the beam irradiation path to 70 degrees or less, the angle of the gas flow path to the material surface can be increased and made closer to a right angle, which allows dust to be collected uniformly on the material surface. , it has become possible to measure dust concentration with high accuracy.

また、材上のダスト沈着層にβ線を照射する
場合、材面に対してβ線をできるだけ直角に近
い角度で照射することが測定精度を向上させる点
で望ましいが、本発明においては気体流路とβ線
照射路との交叉角θを70度以下に形成したことに
より、材面に対するβ線照射路の角度を大きく
して直角により近くすることができ、このためダ
スト濃度を精度良く測定することが可能となつた
ものである。
Furthermore, when irradiating a dust deposited layer on a material with β-rays, it is desirable to irradiate the β-rays at an angle as close to perpendicular to the material surface as possible in order to improve measurement accuracy. By forming the intersection angle θ between the beam and the β-ray irradiation path to 70 degrees or less, the angle of the β-ray irradiation path with respect to the material surface can be increased to be closer to a right angle, making it possible to measure dust concentration with high accuracy. It has become possible to do so.

更に、本発明においては、β線照射路を気体流
路との交差部においてβ線透過性薄膜で閉塞した
ことにより、β線照射路内にダストが侵入して堆
積することが防止され、測定精度の向上及び保守
の簡素化が達成されたものである。
Furthermore, in the present invention, by blocking the β-ray irradiation path with a β-ray permeable thin film at the intersection with the gas flow path, it is possible to prevent dust from entering and accumulating in the β-ray irradiation path. This has resulted in improved accuracy and simplified maintenance.

以下、本発明の一実施例につき第4図を参照し
て説明する。
Hereinafter, one embodiment of the present invention will be described with reference to FIG. 4.

図中1はロール状に巻き取られた材で、この
ロール状材1から繰出された材1aは進行方
行(図中矢印A方向)前方に配設された検出部2
に供給される。この検出部2は直方体状のブロツ
ク主体3を用いて形成されたもので、このブロツ
ク主体3は中央部で水平に2分割された2つのブ
ロツク3a,3bからなる。前記主体3はその上
端面から下端面にかけて前記材1aの幅よりも
小径の被測定気体流路4とβ線照射路5とがそれ
ぞれブロツク主体3の前記2つのブロツク3a,
3bの接合部において交差して穿設されており、
これら流路4及び照射路5のなす角度θは鋭角で
ある約60度に形成されていると共に、流路4との
交差部におけるβ線照射路5は合成樹脂や金属等
によるβ線透過性薄膜6により閉塞されている。
前記流路4の上部側はサンプリングパイプ7の一
端と連結されていると共に、下部側は吸引管8に
より吸引ポンプ9と連結されており、演算制御部
10の制御によりポンプ9を作動させると、被測
定気体がサンプリングパイプ7の他端から吸入さ
れ、流路4、吸引管8を順次通過した後、吸引ポ
ンプ9の吐出部11から外部に放出される。
In the figure, 1 is a material wound into a roll, and the material 1a fed out from this roll-shaped material 1 is detected by a detection unit 2 disposed in front of the traveling direction (direction of arrow A in the figure).
supplied to The detection section 2 is formed using a block main body 3 in the shape of a rectangular parallelepiped, and the block main body 3 consists of two blocks 3a and 3b horizontally divided into two at the center. The main body 3 has a gas flow path 4 to be measured and a β-ray irradiation path 5 having diameters smaller than the width of the material 1a from the upper end surface to the lower end surface of the main body 3, respectively.
3b are intersectingly bored at the joint,
The angle θ formed by the flow path 4 and the irradiation path 5 is approximately 60 degrees, which is an acute angle, and the β-ray irradiation path 5 at the intersection with the flow path 4 is made of synthetic resin, metal, etc. that is transparent to β-rays. It is closed by a thin film 6.
The upper side of the flow path 4 is connected to one end of the sampling pipe 7, and the lower side is connected to a suction pump 9 through a suction pipe 8. When the pump 9 is operated under the control of the arithmetic control section 10, The gas to be measured is sucked in from the other end of the sampling pipe 7 , passes through the flow path 4 and the suction tube 8 in sequence, and then is discharged to the outside from the discharge portion 11 of the suction pump 9 .

また、前記β線照射路5上部には、β線源12
をその内部に収納したβ線源容器13が装着され
ており、前記β線源12から照射路5内に常時β
線が照射されている。更に、β線照射路5の下部
にはβ線検出器14が装着されており、この検出
器14に到達したβ線はここでその到達量に応じ
た電気信号に変換されて演算制御部10に伝送さ
れる。
Further, above the β-ray irradiation path 5, a β-ray source 12 is provided.
A β-ray source container 13 containing a
The line is being irradiated. Furthermore, a β-ray detector 14 is installed at the bottom of the β-ray irradiation path 5, and the β-rays that have reached this detector 14 are converted into electrical signals according to the amount of the β-rays that have arrived at the arithmetic control unit 10. transmitted to.

前記ロール状材1から繰り出されて検出部2
に供給された材1aは、前記ブロツク3a,3
b間に介装されるが、この際に前記記流路4を覆
つて検出部2に装着される。そして、この材1
を移動させるにはブロツク3a,3bを上下に開
き、材1aを移動させた後にブロツク3a,3
bを閉じることにより行なうが、この場合流路4
以外の外部から空気もれがないようにゴムパツキ
ング等の公知の手段で閉塞するものである。次い
で、材1aはピンチローラ15とキヤプスタン
16との間を通つて巻取りロール17に巻取られ
るが、この材1aの移動は制御部10の指示に
従つて駆動されるピンチローラ15によつて行な
われる。なお、18は制御部10と接続された表
示部で、これに測定結果等が表示される。
The detection unit 2 is unrolled from the roll-shaped material 1.
The material 1a supplied to the blocks 3a, 3
b, and at this time, it is attached to the detection unit 2 while covering the flow path 4. And this material 1
To move the material, open the blocks 3a and 3b vertically, move the material 1a, and then open the blocks 3a and 3b.
This is done by closing channel b; in this case, channel 4
It is closed using known means such as rubber packing to prevent air leakage from outside. Next, the material 1a passes between the pinch roller 15 and the capstan 16 and is wound onto the take-up roll 17, but the movement of the material 1a is controlled by the pinch roller 15 driven according to instructions from the control section 10. It is done. Note that 18 is a display unit connected to the control unit 10, on which measurement results and the like are displayed.

次に、上記ダスト計を用いて大気中のダスト濃
度を測定する場合について説明すると、まず被測
定大気採集場所にサンプリングパイプ7の他端部
(図示せず)を配設する。次いで、この状態でβ
線源12から放射され、材1aを透過して検出
器14に到達するβ線量が測定され、この測定値
I0が演算制御部10に一時記憶される。その後、
吸引ポンプ9が作動し、これにより大気の採集が
開始される。即ち、サンプリングパイプ7の他端
から吸入された大気は流路4の上部に流入し、流
路4内を下方に移動するが、この際に流路4を横
断して張設された材1aにより、大気中のダス
トが別されて材1aの上面にダストの沈着層
19が形成される。次いで材1aでダストを
別された大気は、更に流路4を流下して吸引管8
に流入し、ポンプ9を通つて吐出部11から外部
に排出される。ポンプ9が所定時間作動して所定
量の大気が吸引されると、ポンプ9が停止せしめ
られて大気の採集が停止され、この状態において
材1a及びダストの沈着層19を透過して検出
器14に到達するβ線源12からのβ線強度が測
定される。得られた測定値Iは演算制御部10に
送られ、ここで予め記憶された測定値I0を用いて
前記(2)式によりダスト濃度が算出され、表示部1
8に表示される。その後、ブロツク3a,3bが
それぞれ上下に移動されると共に、ピンチローラ
15が駆動されて材1aが進行方向前方(図中
矢印A方向)に所定距離移動する。これにより沈
着層19が流路4外に移動し、流路4内にはダス
トが沈着していない新たな材部分が供給され、
この状態においてブロツク3a,3b間の間隙が
閉じられて最初の状態に復帰する。以後、同様の
動作が繰返されてダスト濃度が測定され続ける
が、これらの動作は全て演算制御部10の指示に
より自動的に行なわれるものである。
Next, a case will be described in which the dust concentration in the atmosphere is measured using the dust meter. First, the other end of the sampling pipe 7 (not shown) is installed at the air sampling location to be measured. Next, in this state β
The β-ray dose emitted from the radiation source 12, transmitted through the material 1a and reaching the detector 14 is measured, and this measured value
I 0 is temporarily stored in the calculation control unit 10. after that,
The suction pump 9 is activated and atmospheric sampling begins. That is, the air sucked in from the other end of the sampling pipe 7 flows into the upper part of the channel 4 and moves downward in the channel 4, but at this time, the material 1a stretched across the channel 4 As a result, dust in the atmosphere is separated and a deposited dust layer 19 is formed on the upper surface of the material 1a. Next, the air from which the dust has been separated by the material 1a flows further down the flow path 4 to the suction pipe 8.
The water flows into the pump 9 and is discharged from the discharge section 11 to the outside through the pump 9. When the pump 9 operates for a predetermined period of time and a predetermined amount of air is sucked, the pump 9 is stopped and the collection of air is stopped. The intensity of β-rays from the β-ray source 12 reaching the target is measured. The obtained measured value I is sent to the arithmetic control section 10, where the dust concentration is calculated by the above equation (2) using the measured value I0 stored in advance, and the dust concentration is displayed on the display section 1.
8 is displayed. Thereafter, the blocks 3a and 3b are moved up and down, respectively, and the pinch roller 15 is driven to move the material 1a a predetermined distance forward in the advancing direction (in the direction of arrow A in the figure). As a result, the deposited layer 19 moves outside the flow path 4, and a new material portion on which no dust is deposited is supplied into the flow path 4.
In this state, the gap between the blocks 3a and 3b is closed, returning to the initial state. Thereafter, similar operations are repeated to continue measuring the dust concentration, but all of these operations are automatically performed according to instructions from the arithmetic control section 10.

本実施例のダスト計は流路4と照射路5とを交
差させると共に、この交差部に材1aに供給す
るようにしたので、この交差部において材1a
を透過するβ線強度I0の測定、大気中のダストの
過、過することにより材面に形成されたダ
スト沈着層19と及び材1aとを透過するβ線
強度Iの測定を材の移動をすることなく行ない
得る。このため、従来法における材の移動誤差
に伴なう測定精度の低下は起り得ず、本ダスト計
の測定精度か高いものである。また、流路4と照
射路5との交差角θは鋭角である60度に形成して
あるので、材面におけるダスト沈着層19は
材面に対して均一に形成されると共に、β線が
材面に直角に近い角度で照射される。このため、
透過β線強度Iは正確に沈着量に対応するものと
なり、測定精度を向上させる。更に、流路4と照
射路5との交差部において照射路5は流路4と薄
膜6で隔離されている。従つて、β線照射路5内
にダストが侵入して堆積することなどが確実に防
止され、測定精度の向上及び保守の簡素化が達成
される。この点を更に詳述すると、本例のダスト
計はβ線透過性薄膜6を設けたことにより、下記
〜の効果が得られたものである。
In the dust meter of this embodiment, the flow path 4 and the irradiation path 5 intersect, and the material 1a is supplied to this intersection, so that the material 1a is supplied to the material 1a at this intersection.
The measurement of the β-ray intensity I0 transmitted through the dust deposited layer 19 formed on the material surface by passing through the dust in the atmosphere, and the β-ray intensity I transmitted through the material 1a. You can do it without having to do it. Therefore, there is no reduction in measurement accuracy due to material movement errors in the conventional method, and the measurement accuracy of this dust meter is high. In addition, since the intersection angle θ between the flow path 4 and the irradiation path 5 is formed at an acute angle of 60 degrees, the dust deposition layer 19 on the material surface is formed uniformly on the material surface, and the β rays are The beam is irradiated at an angle close to perpendicular to the material surface. For this reason,
The transmitted β-ray intensity I accurately corresponds to the amount of deposition, improving measurement accuracy. Further, at the intersection between the flow path 4 and the irradiation path 5, the irradiation path 5 is separated from the flow path 4 by a thin film 6. Therefore, dust is reliably prevented from entering and accumulating in the β-ray irradiation path 5, and improvement in measurement accuracy and simplification of maintenance are achieved. To explain this point in more detail, the dust meter of this example has the following effects by providing the β-ray transparent thin film 6.

β線源及び検出器の汚染防止 β線照射路5内にダストが浸入しないので、
β線源12及び検出器14がダストによつて汚
染されることがなく、このためβ線源12や検
出器14の汚染に起因する測定精度の低下が防
止されると共に、装置の保守も容易になる。
Prevention of contamination of the β-ray source and detector Since dust does not enter the β-ray irradiation path 5,
The β-ray source 12 and detector 14 are not contaminated by dust, which prevents deterioration in measurement accuracy due to contamination of the β-ray source 12 and detector 14, and facilitates maintenance of the device. become.

β線源及び検出器の保護 ポンプ9を作動して測定を行なつている状態
において、β線照射路5は、β線源12側では
ほぼ大気圧状態、検出器14側ではポンプ9の
吸引力によつて負圧状態となつている。従つ
て、測定時には、ポンプ9の吸引力によつて検
出器14に負圧がかかり測定動作が不安定とな
るおそれがあるが、薄膜6によつてこれら防止
される。また、測定中にサンプリングパイプ7
の端部に異物、例えば植物の葉などが付着して
パイプ7を塞ぐと、β線照射路5全体がポンプ
9の吸引力によつて極端な負圧状態になり、β
線源12及び検出器14の両両方にこの負圧が
かかりβ線源の密閉度が破壊される等により、
放射性同位元素による汚染や、検出器の破壊等
が起るおそれがあるが、薄膜6によつてこれら
が防止される。従つて、放射性同位元素を利用
した本装置は、安全性が高いものである。そろ
上、交差部で材1aの移動をすることなくダ
ストの捕集及び測定を行なうため、材の複雑
かつ高精度な移動機構を必要とせず、構成が簡
素化される。
Protection of β-ray Source and Detector When the pump 9 is operated and measurement is performed, the β-ray irradiation path 5 is at almost atmospheric pressure on the β-ray source 12 side, and the pump 9 is under suction on the detector 14 side. It is in a negative pressure state due to the force. Therefore, during measurement, there is a risk that negative pressure will be applied to the detector 14 due to the suction force of the pump 9, making the measurement operation unstable, but this is prevented by the thin film 6. Also, during measurement, the sampling pipe 7
If a foreign object, such as a plant leaf, adheres to the end of the pipe 7 and blocks the pipe 7, the entire β-ray irradiation path 5 becomes extremely negative pressure due to the suction force of the pump 9, and the β-ray
This negative pressure is applied to both the radiation source 12 and the detector 14, destroying the sealing of the β-ray source, etc.
Although there is a risk of contamination with radioactive isotopes and destruction of the detector, the thin film 6 prevents these. Therefore, this device using radioactive isotopes is highly safe. Furthermore, since dust is collected and measured without moving the material 1a at the intersection, a complicated and highly accurate movement mechanism for the material is not required, and the configuration is simplified.

なお、本実施例においては流路4と照射路5の
交差角を60度に形成したが、これに限らず70度以
下の任意の交差角を採用することができ、また流
路4を材1a進行方向に沿つて下向傾斜をもつ
て形成すると共に、照射路5を材1aの進行逆
方向に沿つて下向傾斜をもつて形成したがこれに
限られず、例えば材1aの進行方向と任意の角
度の方向に沿つて下向傾斜をもつて流路4及び照
射路5を形成するようにしても良い。更に、本実
施例においては、ダスト沈着後β線で測定する場
合について説明したが、本ダスト計を用いる時は
刻々の沈着量を連続的又は一定時間おきに測定
し、その表示を行なうことも可能であり、その他
本発明の要旨を逸脱しない範囲で種々変形して差
支えない。
In this example, the intersection angle between the channel 4 and the irradiation channel 5 was formed at 60 degrees, but the intersection angle is not limited to this, and any intersection angle of 70 degrees or less can be adopted. Although the irradiation path 5 is formed with a downward slope along the direction of movement of the material 1a, and the irradiation path 5 is formed with a downward slope along the direction opposite to the direction of movement of the material 1a, the irradiation path 5 is not limited to this. The flow path 4 and the irradiation path 5 may be formed with a downward slope along a direction of an arbitrary angle. Furthermore, in this example, the case of measuring with β rays after dust deposition was explained, but when using this dust meter, the amount of deposited each moment can be measured continuously or at regular intervals, and the measurement can also be displayed. Various modifications may be made without departing from the gist of the present invention.

而して、本発明は、材と被測定気体流路との
交差部にβ線照射路と被測定気体流路と70度以下
の角度で交差させて連結したので、気体流路と
材面との角度が直角により近くなり、ダストの沈
着層が均一になると共に、β線照射路と材面と
の角度も直角により近くなり、このため測定精度
が向上される。また、照射路と流路との交差部に
おいて照射路開口部を薄膜で閉塞したので、照射
路内がダストで汚染されることもなく、測定精度
の向上及び保守の簡易化効果が大きい等の特長を
有する。
Therefore, in the present invention, the β-ray irradiation path and the gas flow path to be measured are connected to each other at an angle of 70 degrees or less at the intersection between the material and the gas flow path to be measured, so that the gas flow path and the material surface are connected to each other at an angle of 70 degrees or less. The angle between the β-ray irradiation path and the material surface becomes closer to a right angle, making the deposited layer of dust uniform, and the angle between the β-ray irradiation path and the material surface becomes closer to a right angle, which improves measurement accuracy. In addition, since the opening of the irradiation path is closed with a thin film at the intersection of the irradiation path and the flow path, the inside of the irradiation path will not be contaminated with dust, which will greatly improve measurement accuracy and simplify maintenance. It has characteristics.

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

第1図乃至第3図はそれぞれ従来のダスト計の
構成を示す説明図、第4図は本発明の一実施例を
示す部分断面側面図である。 1a……材、4……被測定気体流路、5……
β線照射路、6……薄膜、10……演算制御部、
12……β線源、14……β線検出器、19……
沈着層。
1 to 3 are explanatory diagrams showing the configuration of a conventional dust meter, respectively, and FIG. 4 is a partially sectional side view showing an embodiment of the present invention. 1a... Material, 4... Gas flow path to be measured, 5...
β-ray irradiation path, 6... thin film, 10... calculation control unit,
12...β-ray source, 14...β-ray detector, 19...
Deposited layer.

Claims (1)

【特許請求の範囲】[Claims] 1 β線源と、前記β線源から放射されるβ線の
照射路と、前記照射路に供給される材と、前記
材を透過するβ線量を検出する検出器と、前記
検出器の検出する信号を増幅して出力する増幅部
と、前記材と交差する被測定気体流路とからな
り、前記材で被測定気体流路内を流れる被測定
気体を過して被測定気体中の浮遊粉塵を捕集す
ると共に、この捕集した粉塵による材透過β線
の減衰量を前記検出器で検出し、この検出信号を
増幅部で増幅して出力することにより被測定気体
中の浮遊粉塵量を決定するダスト計において、前
記材と被測定気体流路との交差部にβ線照射路
を被測定気体流路と70度以下の角度で交差させて
連結すると共に、β線照射路を被測定気体流路と
の交差部においてβ線透過性薄膜で閉塞してなる
ことを特徴とするダスト計。
1. A β-ray source, an irradiation path for β-rays emitted from the β-ray source, a material supplied to the irradiation path, a detector for detecting the amount of β-rays transmitted through the material, and detection by the detector. It consists of an amplification unit that amplifies and outputs a signal to be measured, and a gas flow path to be measured that intersects with the material, and the material passes through the gas flowing through the gas flow path to detect floating air in the gas to be measured. At the same time as collecting dust, the amount of attenuation of β-rays passing through the material due to the collected dust is detected by the detector, and this detection signal is amplified by the amplifier and output, thereby determining the amount of suspended dust in the gas to be measured. In the dust meter that determines the A dust meter characterized in that the intersection with a measurement gas flow path is blocked with a β-ray permeable thin film.
JP4233382A 1982-03-17 1982-03-17 Dust meter Granted JPS58160806A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4233382A JPS58160806A (en) 1982-03-17 1982-03-17 Dust meter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4233382A JPS58160806A (en) 1982-03-17 1982-03-17 Dust meter

Publications (2)

Publication Number Publication Date
JPS58160806A JPS58160806A (en) 1983-09-24
JPH0233964B2 true JPH0233964B2 (en) 1990-07-31

Family

ID=12633075

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4233382A Granted JPS58160806A (en) 1982-03-17 1982-03-17 Dust meter

Country Status (1)

Country Link
JP (1) JPS58160806A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61241640A (en) * 1985-04-19 1986-10-27 Denki Kagaku Keiki Co Ltd Method and apparatus for filter collection type measurement of concentration of granular material
JPS6255548A (en) * 1985-09-05 1987-03-11 Aloka Co Ltd Beta ray absorption type continuously floating dust measurement
JP6586929B2 (en) * 2016-07-29 2019-10-09 東亜ディーケーケー株式会社 measuring device
CN109164118B (en) * 2018-08-08 2022-04-05 北京雪迪龙科技股份有限公司 Calibration system and method of beta absorption type dust meter

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS625647Y2 (en) * 1978-03-15 1987-02-09

Also Published As

Publication number Publication date
JPS58160806A (en) 1983-09-24

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