JPH11118701A - Environmental monitoring device - Google Patents
Environmental monitoring deviceInfo
- Publication number
- JPH11118701A JPH11118701A JP9276862A JP27686297A JPH11118701A JP H11118701 A JPH11118701 A JP H11118701A JP 9276862 A JP9276862 A JP 9276862A JP 27686297 A JP27686297 A JP 27686297A JP H11118701 A JPH11118701 A JP H11118701A
- Authority
- JP
- Japan
- Prior art keywords
- environment
- detection means
- detecting means
- distance
- emission point
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
- Y02E30/30—Nuclear fission reactors
Landscapes
- Sampling And Sample Adjustment (AREA)
- Monitoring And Testing Of Nuclear Reactors (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は環境監視装置に係わ
り、特に化学工場や原子力プラント,再処理工場等の緊
急時に環境中へ放出された場合、環境へ影響を与える恐
れのある物質を取り扱う工場やプラントで利用するに好
適な環境監視装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an environmental monitoring apparatus, and more particularly to a factory that handles substances that may affect the environment when released into the environment in an emergency, such as a chemical factory, a nuclear plant, and a reprocessing factory. And an environment monitoring device suitable for use in a plant.
【0002】[0002]
【従来の技術】一般に、環境へ影響を与える恐れのある
大気汚染物質を扱う工場やプラントから環境中へ放出さ
れた物質の環境濃度を測定するため、環境監視装置とし
て環境中にモニタリングポストやモニタリングステーシ
ョンと呼ばれる放出物質の濃度や風向,風速を測定する
検出手段が設置される。万一、環境へ係る物質が放出さ
れた場合、すなわち緊急時には、これらの検出手段から
得られたデータに基づき、拡散状況や濃度を把握し環境
への影響を評価して適切な対応を取る必要がある。2. Description of the Related Art Generally, a monitoring post or monitoring is performed as an environmental monitoring device in an environment to measure the environmental concentration of a substance released into the environment from a factory or a plant that handles air pollutants that may affect the environment. A detecting means for measuring the concentration, the wind direction, and the wind speed of the emission substance called a station is provided. Should any substance related to the environment be released, that is, in an emergency, it is necessary to grasp the diffusion status and concentration based on the data obtained from these detection means, evaluate the impact on the environment, and take appropriate measures. There is.
【0003】このため、このような検出手段は環境中に
適切に配置されねばならない。従来、図3に示すように
工場やプラント周辺に配置される前記検出手段は、想定
される放出点を中心として、4〜16方位に1点程度の
間隔で配置されていた。そして、これらの検出手段によ
り検出された濃度の分布から拡散状況を把握し、環境へ
の影響を評価する装置となっていた。この種の技術とし
て特開平2−64437号公報を挙げることができる。[0003] For this reason, such detection means must be appropriately arranged in the environment. Conventionally, as shown in FIG. 3, the detection means arranged around a factory or a plant has been arranged at an interval of about one point in 4 to 16 directions around an assumed emission point. In addition, the apparatus has been designed to grasp the state of diffusion from the distribution of the concentration detected by these detecting means and evaluate the effect on the environment. Japanese Unexamined Patent Publication No. 2-64437 can be mentioned as this kind of technology.
【0004】[0004]
【発明が解決しようとする課題】一般に、環境中へ放出
された物質の拡散状況は、図5に水平方向に対し一例を
示す大気安定度(A〜F)毎に拡散物質の拡散幅の標準
偏差を実験的に放出点からの距離でまとめたPasquill−
Giffordの線図により予測可能である。In general, the state of diffusion of a substance released into the environment is shown in FIG. 5 as an example in the horizontal direction. Pasquill −
This can be predicted from the Gifford diagram.
【0005】[0005]
【表1】 [Table 1]
【0006】この線図から拡散幅を求める際に必要とな
る大気安定度は、表1のPasquillの安定度分類により、
風速や日射量,雲量等の気象条件から定められる。放出
点から風に乗り環境中へ拡散する物質は、図6に模式的
に示すように環境中に拡がり、その拡散物質の拡がり幅
の標準偏差が前記Pasquill−Gifford の線図から評価さ
れる。環境中に放出された物質の濃度分布は図7に示す
ような正規分布に従う。[0006] The atmospheric stability required for obtaining the diffusion width from this diagram is calculated according to the Pasquill stability classification shown in Table 1.
It is determined from weather conditions such as wind speed, solar radiation, and cloudiness. Substances that diffuse into the environment by wind from the point of release spread into the environment, as schematically shown in FIG. 6, and the standard deviation of the spread width of the diffused substances is evaluated from the Pasquill-Gifford diagram. The concentration distribution of the substance released into the environment follows a normal distribution as shown in FIG.
【0007】放出点からの距離r(m)における拡散幅の
標準偏差をσ(r)(m)とすると、距離rにおける拡散物
質の拡がりの約95%区間は±2σ(r)、約99%区間
は±3σ(r)の範囲に存在する。図8は、統計の分野で
一般的に用いられる約95%区間を考え、各大気安定度
に対応する±2σ(r)、すなわち4σ(r)の幅と、16
方位で半径rの円周上に検出手段を配置した際の検出手
段間の距離を比較したものである。図8より大気安定度
がA〜Bの場合には、16方位程度に配置した検出手段
により、環境中に放出された物質の拡がりを捉えること
が可能である。Assuming that the standard deviation of the diffusion width at a distance r (m) from the emission point is σ (r) (m), about 95% of the spread of the diffusion material at the distance r is ± 2σ (r) and about 99%. The% section exists in a range of ± 3σ (r). FIG. 8 shows a range of ± 2σ (r) corresponding to each atmospheric stability, that is, a range of 4σ (r), considering an approximately 95% section generally used in the field of statistics.
This is a comparison of the distance between the detection means when the detection means is arranged on the circumference of the radius r in the azimuth. As shown in FIG. 8, when the atmospheric stability is A to B, it is possible to detect the spread of the substance released into the environment by the detecting means arranged in about 16 directions.
【0008】しかし、大気安定度がC〜Fの場合には放
出された物質の拡がりを捉えることが困難となり環境中
の濃度を測定できない場合が起こりうることが示唆され
る。すなわち、環境監視装置において検出手段が適切に
配置されていない場合、すべての気象条件を考慮すると
環境中へ放出された物質が環境中へ配置された検出手段
と検出手段の間を擦り抜ける状況が発生しうることが懸
念される。[0008] However, when the atmospheric stability is C to F, it is difficult to grasp the spread of the released substance, and it is suggested that the concentration in the environment may not be measured. That is, when the detection means is not properly arranged in the environment monitoring device, a situation in which the substance released into the environment slips between the detection means arranged in the environment and the detection means in consideration of all weather conditions. There is a concern that this may occur.
【0009】[0009]
【課題を解決するための手段】このような課題を解決す
るために、本発明の環境監視装置では前記の気象条件か
ら定まる大気安定度より与えられる環境中へ放出された
物質の拡散幅を考慮し、環境中へ検出手段を配置するよ
うにしている。In order to solve such a problem, the environmental monitoring device of the present invention considers the diffusion width of a substance released into the environment given by the atmospheric stability determined from the above-mentioned weather conditions. Then, the detecting means is arranged in the environment.
【0010】すなわち、放出点から第1の検出手段まで
の距離をr(m),距離rにおける放出物質の拡散幅の標
準偏差をσ(r)(m)とするとき、前記放出点と他の検出
手段とを結ぶ直線上の放出点からの距離rの点のうち、
前記放出点と第1の検出手段がなす直線に隣接する直線
上にある点と、前記第1の検出手段間の距離を2σ(r)
以内もしくは3σ(r)以内となるように検出手段を配置
する。ここで、σ(r)の範囲は次式で与えられる。That is, when the distance from the emission point to the first detecting means is r (m), and the standard deviation of the diffusion width of the emission material at the distance r is σ (r) (m), the emission point is defined as Of points at a distance r from the emission point on the straight line connecting the detection means
A distance between a point on a straight line adjacent to a straight line formed by the emission point and the first detection means and a distance between the first detection means and 2σ (r)
The detection means is arranged so as to be within 3σ (r). Here, the range of σ (r) is given by the following equation.
【0011】[0011]
【数1】0.05r0.8≦σ(r)≦0.3r0.92 上記の不等式は、大気安定度A〜Fに対し、図5に示し
たPasquill−Giffordの線図を最小自乗法により、相関
係数0.98 以上においてべき乗型の式で近似したもの
である。0.05r 0.8 ≦ σ (r) ≦ 0.3r 0.92 The above inequality is obtained by applying the Pasquill-Gifford diagram shown in FIG. This is an approximation of the relational number 0.98 or higher by a power-type equation.
【0012】また、前記課題は、放出点と他の検出手段
とを結ぶ直線のうち、前記第1の検出手段に隣接する直
線と放出点と前記第1の検出手段を結ぶ直線がなす角度
をθとする時、角度θが2sin-1{σ(r)/r}以内、
もしくは2sin-1{3σ(r)/2r}以内となるように
検出手段を配置することによっても解決される。In addition, the problem is that, of the straight lines connecting the emission point and the other detection means, the angle formed by the straight line adjacent to the first detection means and the straight line connecting the emission point and the first detection means is formed. θ, the angle θ is within 2 sin -1 {σ (r) / r},
Alternatively, the problem can be solved by arranging the detecting means so as to be within 2 sin -1 {3σ (r) / 2r}.
【0013】さらに、放出点と他の検出手段とを結ぶ直
線上の放出点からの距離rの点のうち、前記放出点と第
1の検出手段がなす直線に隣接する直線上にある点と、
前記第1の検出手段間の距離を4σ(r)以内もしくは6
σ(r)以内となるように検出手段を配置することによっ
ても解決される。また、放出点と他の検出手段とを結ぶ
直線のうち、前記第1の検出手段に隣接する直線と放出
点と前記第1の検出手段を結ぶ直線がなす角度θとする
時、角度θが2sin-1{2σ(r)/r}以内、もしくは
2sin-1{3σ(r)/r}以内となるように検出手段を
配置する場合にも同様である。Further, of the points at a distance r from the emission point on a straight line connecting the emission point and the other detection means, a point on a straight line adjacent to the emission point and the straight line formed by the first detection means. ,
The distance between the first detecting means is within 4σ (r) or 6
The problem can also be solved by arranging the detecting means so as to be within σ (r). In addition, among the straight lines connecting the emission point and the other detection means, the angle θ is defined as an angle θ formed by a straight line connecting the emission point and the first detection means and a straight line adjacent to the first detection means. The same applies to the case where the detecting means is arranged so as to be within 2 sin -1 {2σ (r) / r} or within 2 sin -1 {3σ (r) / r}.
【0014】また、前記の環境中に配置された検出手段
は、その位置を環境中に固定された固定検出手段と、環
境中を移動可能な移動検出手段を組み合わせて構成する
ことを可能としている。移動検出手段を組み合わせる場
合、気象予測手段と拡散予測手段、または気象観測手段
と拡散予測手段により環境中へ放出された物質の拡散範
囲を予測し、移動検出手段へ放出された物質の拡散範囲
と移動位置を指示,表示し、移動検出手段が適切な位置
へ移動し、濃度を測定するようにしている。The detecting means arranged in the environment can be constructed by combining a fixed detecting means whose position is fixed in the environment and a movement detecting means movable in the environment. . When the movement detection means is combined, the weather prediction means and the diffusion prediction means, or the weather observation means and the diffusion prediction means predict the diffusion range of the substance released into the environment, and the diffusion range of the substance released to the movement detection means The movement position is indicated and displayed, and the movement detection means moves to an appropriate position to measure the concentration.
【0015】[0015]
【発明の実施の形態】以下、本発明の実施の形態を図面
を用いて説明する。Embodiments of the present invention will be described below with reference to the drawings.
【0016】本発明の環境監視装置における検出手段の
配置の実施例1を図1に示す。放出点5の周りに、放出
点から環境中へ拡散する恐れのある物質の濃度や、風
向,風速等の気象データを測定する固定検出手段1,
2,3が配置されている。本実施例ではその時の風向6
から、放出された物質は固定検出手段1と2の間を拡散
するため、移動検出手段4を放出点の風下へ配置してい
る。FIG. 1 shows a first embodiment of the arrangement of the detecting means in the environment monitoring apparatus of the present invention. Around the emission point 5, fixed detection means 1 for measuring the concentration of a substance which may diffuse from the emission point into the environment and weather data such as wind direction and wind speed.
2, 3 are arranged. In this embodiment, the wind direction at that time is 6
Therefore, the movement detection means 4 is arranged on the lee of the release point in order to diffuse the substance released from the fixed detection means 1 and 2.
【0017】この場合、放出点と移動検出手段4とを結
ぶ直線上の放出点からの距離rの点と前記固定検出手段
1または2間の距離dを(数1)より求められる拡散幅
の標準偏差σ(r)から2σ(r)以内もしくは3σ(r)以
内としている。前記の距離dを2σ(r)以内とすること
により、放出物質の拡がりの約95%の区間内に少なく
とも2点の検出手段が配置され、放出物質の濃度を測定
可能である。また、前記の距離dを3σ(r)以内とする
と、放出物質の拡がりの約99%の区間内に少なくとも
2点の検出手段が配置される。移動検出手段4は、濃度
や風向・風速等の検出機器を搭載した自動車やあらかじ
め設定された軌道上を走行する軌道車輌などを適用可能
である。In this case, the point of the distance r from the emission point on the straight line connecting the emission point and the movement detection means 4 and the distance d between the fixed detection means 1 and 2 are defined by the diffusion width of It is within 2σ (r) or 3σ (r) from the standard deviation σ (r). By setting the distance d within 2σ (r), at least two detection means are arranged in a section of about 95% of the spread of the emitted substance, and the concentration of the emitted substance can be measured. If the distance d is within 3σ (r), at least two detection means are arranged in a section of about 99% of the spread of the emission material. The movement detecting means 4 can be applied to an automobile equipped with a device for detecting the concentration, the wind direction, the wind speed, and the like, a track vehicle running on a preset track, or the like.
【0018】次に、本発明の環境監視装置における検出
手段の配置の実施例2を図2に示す。放出点5の周り
に、放出点5から環境中へ拡散する恐れのある物質の濃
度や、風向,風速等の気象データを測定する固定検出手
段1,2,3を配置し、移動検出手段4が放出点5の風
下へ配置されている。この場合、放出点5と固定検出手
段1または2を結ぶ直線と放出点と移動検出手段4を結
ぶ直線がなす角度をθとする時、角度θが2sin-1{σ
(r)/r}以内、もしくは2sin-1{3σ(r)/2r}以内
となるように配置している。前記の角度θを2sin-1{σ
(r)/r}以内とすることにより、放出物質の拡がりの
約95%の区間内に少なくとも2点の検出手段が配置さ
れる。また、前記の角度θを2sin-1{3σ(r)/2r}
以内にすると、放出物質の拡がりの約99%の区間内に
少なくとも2点の検出手段が配置され、放出物質を捉え
ることが可能である。Next, a second embodiment of the arrangement of the detecting means in the environment monitoring apparatus of the present invention is shown in FIG. Around the emission point 5, fixed detection means 1, 2, 3 for measuring the concentration of a substance which may diffuse from the emission point 5 into the environment and weather data such as wind direction and wind speed are arranged, and the movement detection means 4 is provided. Is located leeward of the discharge point 5. In this case, assuming that an angle between a straight line connecting the emission point 5 and the fixed detection means 1 or 2 and a straight line connecting the emission point and the movement detection means 4 is θ, the angle θ is 2 sin −1 {σ
(r) / r} or 2 sin -1 {3σ (r) / 2r}. The angle θ is 2 sin −1 {σ
By setting it within (r) / r}, at least two detection means are arranged in a section of about 95% of the spread of the emitted substance. Further, the angle θ is set to 2 sin −1 {3σ (r) / 2r}.
Within this range, at least two detecting means are arranged in a section of about 99% of the spread of the emitted substance, and the emitted substance can be captured.
【0019】本発明の環境監視装置における検出手段の
配置の実施例3を図9に示す。放出点5の周りに、放出
点から環境中へ拡散する恐れのある物質の濃度や、風
向,風速等の気象データを測定する固定検出手段1,
2,3を配し、移動検出手段4を放出点の風下へ配置し
ている。この場合、放出点と移動検出手段4とを結ぶ直
線上の放出点からの距離rの点と前記固定検出手段1ま
たは2間の距離dを4σ(r)以内もしくは6σ(r)以内
としている。前記の距離dを4σ(r)以内とすることに
より、放出物質の拡がりの約95%の区間内に少なくと
も1点の検出手段が配置され、放出物質の濃度を測定可
能である。また、前記の距離dを6σ(r)以内とする
と、放出物質の拡がりの約99%の区間内に少なくとも
1点の検出手段が配置される。FIG. 9 shows a third embodiment of the arrangement of the detecting means in the environment monitoring apparatus of the present invention. Around the emission point 5, fixed detection means 1 for measuring the concentration of a substance which may diffuse from the emission point into the environment and weather data such as wind direction and wind speed.
2 and 3 are arranged, and the movement detecting means 4 is arranged leeward of the discharge point. In this case, the distance d between the fixed point detecting means 1 and the distance r from the point of emission on the straight line connecting the emission point and the movement detecting means 4 is within 4σ (r) or within 6σ (r). . By setting the distance d within 4σ (r), at least one detecting means is arranged within a section of about 95% of the spread of the emitted substance, and the concentration of the emitted substance can be measured. If the distance d is within 6σ (r), at least one detecting means is disposed in a section of about 99% of the spread of the emission material.
【0020】次に、本発明の環境監視装置における検出
手段の配置の実施例4を図10に示す。放出点5の周り
に、放出点5から環境中へ拡散する恐れのある物質の濃
度や、風向,風速等の気象データを測定する固定検出手
段1,2,3を配置し、移動検出手段4が放出点5の風
下へ配置されている。この場合、放出点5と固定検出手
段1または2を結ぶ直線と放出点と移動検出手段4を結
ぶ直線がなす角度をθとする時、角度θが2sin-1{2σ
(r)/r}以内、もしくは2sin-1{3σ(r)/r}以内
となるように配置している。前記の角度θを2sin-1{2
σ(r)/r}以内とすることにより、放出物質の拡がり
の約95%の区間内に少なくとも1点の検出手段が配置
される。また、前記の角度θを2sin-1{3σ(r)/r}
にすると、放出物質の拡がりの約99%の区間内に少な
くとも1点の検出手段が配置され、放出物質を捉えるこ
とが可能である。Next, FIG. 10 shows a fourth embodiment of the arrangement of the detecting means in the environment monitoring apparatus of the present invention. Around the emission point 5, fixed detection means 1, 2, 3 for measuring the concentration of a substance which may diffuse from the emission point 5 into the environment and weather data such as wind direction and wind speed are arranged, and the movement detection means 4 is provided. Is located leeward of the discharge point 5. In this case, assuming that the angle between the straight line connecting the emission point 5 and the fixed detection means 1 or 2 and the straight line connecting the emission point and the movement detection means 4 is θ, the angle θ is 2 sin −1 {2σ
(r) / r} or within 2 sin −1 {3σ (r) / r}. The angle θ is 2 sin −1 {2
By setting it within σ (r) / r}, at least one detecting means is arranged in a section of about 95% of the spread of the emitted substance. Further, the angle θ is set to 2 sin −1 {3σ (r) / r}
Then, at least one detecting means is arranged in a section of about 99% of the spread of the emitted substance, and the emitted substance can be captured.
【0021】本発明の環境監視装置のブロック図を図1
1に示す。工場やプラント等の施設、すなわち放出点周
りの環境中には固定検出手段1,2,3と移動検出手段
4が配置されている。本環境監視装置では、気象データ
として気象庁等の提供する気象観測値や数値予測デー
タ,施設内の気象観測手段からのデータを気象データ収
集装置により収集する。収集された気象データに基づ
き、気象解析装置は、風速,風向(風速ベクトル)や温
度,湿度,雨量等の気象に関わる施設周辺や監視対象範
囲内の分布を求める。FIG. 1 is a block diagram of an environment monitoring apparatus according to the present invention.
It is shown in FIG. Stationary detection means 1, 2, 3 and movement detection means 4 are arranged in a facility such as a factory or a plant, that is, in the environment around the emission point. In this environment monitoring device, a meteorological data collection device collects, as weather data, weather observation values and numerical prediction data provided by the Japan Meteorological Agency and data from weather observation means in the facility. Based on the collected meteorological data, the meteorological analyzer obtains distributions around the facility related to weather, such as wind speed, wind direction (wind speed vector), temperature, humidity, and rainfall, and within a monitoring target range.
【0022】気象データや気象解析データは必要に応
じ、表示・出力される。施設において、何らかの異常が
発生し、環境に影響を与える恐れのある物質の放出が懸
念される場合、拡散解析装置では、放出点における放出
濃度を単位濃度に規格化し、拡散解析を実施する。その
結果に基づく拡散状況や、放出点濃度で規格化された濃
度分布等の解析データは制御・管理装置により表示され
るとともに、移動検出手段4へ伝送される。移動検出手
段4へ伝送された解析データは、移動検出手段4内で表
示され、測定に適した位置が指示される。移動検出手段
4は、この表示,指示に基づき、放出物質の拡散範囲内
へ移動し、濃度等のデータを計測する。Weather data and weather analysis data are displayed and output as needed. If any abnormality occurs in the facility and there is a concern about release of a substance that may affect the environment, the diffusion analyzer normalizes the release concentration at the release point to a unit concentration and performs a diffusion analysis. Analytical data such as the diffusion state based on the result and the concentration distribution standardized by the emission point concentration are displayed by the control / management device and transmitted to the movement detecting means 4. The analysis data transmitted to the movement detecting means 4 is displayed in the movement detecting means 4, and a position suitable for measurement is specified. The movement detecting means 4 moves into the diffusion range of the emission substance based on the display and instruction, and measures data such as concentration.
【0023】固定検出手段1,2,3及び移動検出手段
4の測定結果は、制御・管理装置へ伝送され、環境中で
測定されたデータに基づき、前記の拡散解析装置で計算
された放出点濃度で規格化された濃度分布を、実際の値
に変換する。これにより、環境中の濃度分布が評価可能
となるとともに、放出点での放出濃度が求められる。こ
れにより、環境中へ放出された物質の拡散状況や濃度分
布が評価でき、緊急時に適切な対策を取るためのデータ
が提供される。The measurement results of the fixed detection means 1, 2, 3, and the movement detection means 4 are transmitted to the control and management device, and the emission point calculated by the diffusion analysis device based on the data measured in the environment. The density distribution standardized by the density is converted to an actual value. As a result, the concentration distribution in the environment can be evaluated, and the emission concentration at the emission point is determined. As a result, the state of diffusion and concentration distribution of substances released into the environment can be evaluated, and data for taking appropriate measures in an emergency can be provided.
【0024】前述のように移動検出手段4は、濃度や風
向・風速等の検出機器を搭載した自動車やあらかじめ設
定された軌道上を走行する軌道車輌などを適用可能であ
る。また、これらの移動検出手段は有人の車輌や制御・
管理装置などで制御される無人車輌により実現できる。
さらに、移動検出手段4と制御・管理装置間の情報の伝
送や移動検出手段4の制御は有線,無線により達成可能
である。As described above, the movement detecting means 4 can be applied to an automobile equipped with a device for detecting the concentration, the wind direction, the wind speed, and the like, or a track vehicle running on a predetermined track. In addition, these movement detection means can be used for manned vehicles,
It can be realized by an unmanned vehicle controlled by a management device or the like.
Further, transmission of information between the movement detection means 4 and the control / management device and control of the movement detection means 4 can be achieved by wire or wirelessly.
【0025】図12は、拡散解析装置の解析結果を制御
・管理装置が移動検出手段等に表示する際の表示例であ
る。放出点5となる工場やプラント等の主要な形状,等
高線などの主要な地形情報11,平均的な風向,風速
6,固定検出手段3の配置が画面上に表示される。解析
データにおける拡散状況や濃度分布に基づき、放出・拡
散物質の拡がり8が表示され、移動検出手段4への移動
指示位置9が放出・拡散物質の拡がり8の中央部に示さ
れている。FIG. 12 is a display example when the control / management device displays the analysis result of the diffusion analysis device on the movement detecting means or the like. The main shapes of factories and plants serving as the emission points 5, the main terrain information 11 such as contour lines, the average wind direction, the wind speed 6, and the arrangement of the fixed detection means 3 are displayed on the screen. The spread 8 of the released / diffused substance is displayed based on the diffusion state and the concentration distribution in the analysis data, and the movement instruction position 9 to the movement detecting means 4 is shown at the center of the spread 8 of the released / diffused substance.
【0026】本実施例では、放出・拡散物質の拡がり8
の範囲内に固定検出器3が存在しないため、固定検出器
の間を補完する形で、移動検出器4が放出・拡散物質の
拡がり8を捉え、濃度を測定している。拡散解析装置に
おける放出点における放出濃度で規格化した計算は、解
析範囲内で一様な風向・風速が想定され、地形が比較的
平坦な場合、以下のガウス・プリュームモデルに基づく
解析解を用いることにより容易に実施可能である。In the present embodiment, the spread of the emitted / diffused material 8
Since the fixed detector 3 does not exist within the range, the moving detector 4 captures the spread 8 of the emitted / diffused substance and measures the concentration in a manner that complements the space between the fixed detectors. In the calculation normalized by the emission concentration at the emission point in the diffusion analysis device, when the uniform wind direction and wind speed are assumed within the analysis range and the terrain is relatively flat, the analytical solution based on the following Gaussian plume model is used This can be easily implemented.
【0027】[0027]
【数2】 (Equation 2)
【0028】ここで、χ(x,y,z)は空間濃度、qは
単位時間当りの拡散物質の放出量、uは風速、σy ,σ
z は水平及び鉛直方向の拡散幅の標準偏差、Hは放出高
さ、xは風向き水平方向座標、yはxに直交する水平方
向座標、zは鉛直方向座標である。Here, χ (x, y, z) is the spatial density, q is the amount of diffused substance released per unit time, u is the wind speed, σ y , σ
z is the standard deviation of the horizontal and vertical diffusion widths, H is the emission height, x is the wind horizontal coordinate, y is the horizontal coordinate orthogonal to x, and z is the vertical coordinate.
【0029】一方、解析範囲内で風向・風速が一様では
なく、地形の影響も考慮しなければならない場合には、
図13に模式的に示した多数の疑似粒子を放出し追跡す
る疑似粒子追跡法により拡散解析が可能である。本手法
による疑似粒子の挙動は次式に基づき追跡される。On the other hand, when the wind direction and the wind speed are not uniform within the analysis range and the influence of the terrain must be considered,
Diffusion analysis is possible by the pseudo particle tracking method of releasing and tracking a large number of pseudo particles schematically shown in FIG. The behavior of the quasi-particles by this method is tracked based on the following equation.
【0030】[0030]
【数3】X(t)=X(t)+ΔtU ここで、X(t)は時刻tにおける粒子の位置、Uは疑似
粒子の移動速度、Δtは計算における時間刻み幅であ
る。また、Uは粒子位置における平均風速Uw,風速の
乱流変動量UD 等からなるベクトル量であり、気象解析
の結果に従い求められる。この手法では、放出物質の放
出率に対応した量を個々の疑似粒子に与え、計算格子が
構成する体積内の粒子数を計算し換算することにより大
気中の濃度が求められる。単位時間当りの拡散物質の放
出量をq,時間刻み幅当りに放出する疑似粒子の個数を
nとすれば、空間濃度χ(x,y,z)は次式で与えられ
る。X (t) = X (t) + ΔtU where X (t) is the position of the particle at time t, U is the moving speed of the pseudo particle, and Δt is the time step in the calculation. Further, U is the mean wind velocity Uw, vector quantity comprised of turbulent fluctuation amount U D like wind speed in the particle position, determined in accordance with a result of the weather analysis. In this method, an amount corresponding to the emission rate of the emitted substance is given to each pseudo particle, and the number of particles in the volume constituted by the calculation grid is calculated and converted, thereby obtaining the concentration in the atmosphere. Assuming that the amount of diffused substance released per unit time is q and the number of pseudo particles released per time step is n, the spatial concentration χ (x, y, z) is given by the following equation.
【0031】[0031]
【数4】 (Equation 4)
【0032】ここで、Nは位置(x,y,z)のセル内
に含まれる粒子数、Δx,Δy,Δzは濃度計算におけ
る計算セル幅である。Here, N is the number of particles contained in the cell at the position (x, y, z), and Δx, Δy, and Δz are calculation cell widths in the density calculation.
【0033】[0033]
【発明の効果】本発明の環境監視装置では、気象条件か
ら定まる環境中へ放出された物質の拡散幅を考慮し、環
境中の固定検出手段や移動検出手段間の間隔や、放出点
と検出手段がなす直線間の角度を適切に設定する。これ
により、ほとんどの気象条件下において常に少なくとも
1つないし2つの検出手段が環境中へ放出された物質の
拡がりを捉え、濃度を測定可能となる。このため、環境
中へ放出された物質が環境中へ配置された検出手段と検
出手段の間を擦り抜けるという懸念が解消される。According to the environmental monitoring apparatus of the present invention, the distance between the fixed detection means and the movement detection means in the environment, the emission point, and the distance between the fixed detection means and the movement detection means in the environment are considered in consideration of the diffusion width of the substance released into the environment determined from the weather conditions. The angle between the straight lines formed by the means is set appropriately. Thus, under most weather conditions, at least one or two detection means can always detect the spread of the substance released into the environment and measure the concentration. For this reason, the concern that the substance released into the environment will slip through between the detecting means arranged in the environment and the detecting means is solved.
【0034】さらに、本発明の環境監視装置では気象予
測手段と拡散予測手段、または気象観測手段と拡散予測
手段により環境中へ放出された物質の拡散範囲を予測
し、移動検出手段へ放出された物質の拡散範囲と移動位
置を指示,表示する。これにより、移動検出手段が放出
物質の拡散状況に応じた適切な位置へ移動し、濃度を測
定可能となる。Further, in the environment monitoring device of the present invention, the diffusion range of the substance released into the environment is predicted by the weather prediction means and the diffusion prediction means, or the weather observation means and the diffusion prediction means, and released to the movement detection means. Indicate and display the diffusion range and movement position of the substance. Thereby, the movement detecting means moves to an appropriate position according to the diffusion state of the released substance, and the concentration can be measured.
【図1】本発明の実施例1である環境監視装置における
検出手段の配置を示す図。FIG. 1 is a diagram showing an arrangement of detection means in an environment monitoring device according to a first embodiment of the present invention.
【図2】本発明の実施例2である環境監視装置における
検出手段の配置を示す図。FIG. 2 is a diagram showing an arrangement of detection means in an environment monitoring device according to a second embodiment of the present invention.
【図3】従来の環境監視装置における検出手段の配置例
を示す図。FIG. 3 is a diagram showing an example of the arrangement of detection means in a conventional environment monitoring device.
【図4】従来の環境監視装置における検出手段の配置に
おける濃度分布測定結果を示す特性図。FIG. 4 is a characteristic diagram showing a concentration distribution measurement result in an arrangement of detection means in a conventional environment monitoring device.
【図5】Pasquill−Giffordの線図(水平方向拡散
幅)。FIG. 5 is a Pasquill-Gifford diagram (horizontal diffusion width).
【図6】拡散物質の拡がりの概念図。FIG. 6 is a conceptual diagram of spreading of a diffusion material.
【図7】拡散物質の濃度分布を示す特性図。FIG. 7 is a characteristic diagram showing a concentration distribution of a diffusion substance.
【図8】拡散物質の拡がりの95%区間と方位の幅の比
較との関係を示す特性図。FIG. 8 is a characteristic diagram showing a relationship between a 95% section of the spread of the diffusion material and a comparison of the width of the azimuth.
【図9】本発明の実施例3である環境監視装置における
検出手段の配置を示す図。FIG. 9 is a diagram showing an arrangement of detection means in the environment monitoring device according to the third embodiment of the present invention.
【図10】本発明の実施例4である環境監視装置におけ
る検出手段の配置を示す図。FIG. 10 is a diagram showing an arrangement of detection means in the environment monitoring device according to the fourth embodiment of the present invention.
【図11】本発明の環境監視装置による環境監視のブロ
ック図。FIG. 11 is a block diagram of environment monitoring by the environment monitoring device of the present invention.
【図12】本発明の環境監視装置における放出物質の拡
散範囲と移動位置の指示,表示例を示す図。FIG. 12 is a diagram showing an example of indication and display of a diffusion range and a movement position of a released substance in the environment monitoring device of the present invention.
【図13】疑似粒子による拡散予測の概念図。FIG. 13 is a conceptual diagram of diffusion prediction using pseudo particles.
1,2,3…固定検出手段、4…移動検出手段、5…放
出点、6…風向、7…16方位、8…放出・拡散物質の
拡がり、9…移動検出手段への移動指示位置、10…疑
似粒子、11…等高線等の地形情報。1, 2, 3 ... fixed detection means, 4 ... movement detection means, 5 ... emission point, 6 ... wind direction, 7 ... 16 directions, 8 ... spread of emitted / diffused substances, 9 ... movement instruction position to movement detection means, 10: pseudo particle, 11: topographic information such as contour lines.
Claims (7)
検出手段を環境中に配置した環境監視装置において、放
出点から第1の検出手段までの距離をr(m),距離rに
おける放出物質の拡散幅の標準偏差をσ(r)(m)とする
とき、前記放出点と他の検出手段とを結ぶ直線上の放出
点からの距離rの点のうち、前記放出点と第1の検出手
段がなす直線に隣接する直線上にある点と、前記第1の
検出手段間の距離を2σ(r)以内もしくは3σ(r)以内
とすることを特徴とする環境監視装置。ここで、σ(r)
の範囲は次式で与えられる。 0.05r0.8≦σ(r)≦0.3r0.92 1. An environment monitoring apparatus in which detection means for detecting the concentration of a substance released into the environment is disposed in the environment, wherein the distance from the release point to the first detection means is represented by r (m) and distance r. When the standard deviation of the diffusion width of the emission material is σ (r) (m), among the points at a distance r from the emission point on a straight line connecting the emission point and other detection means, the emission point and the second An environment monitoring device, wherein a distance between a point on a straight line adjacent to a straight line formed by the first detecting means and the first detecting means is within 2σ (r) or within 3σ (r). Where σ (r)
Is given by the following equation. 0.05r 0.8 ≦ σ (r) ≦ 0.3r 0.92
検出手段を環境中に配置した環境監視装置において、放
出点から第1の検出手段までの距離をr(m),距離rに
おける放出物質の拡散幅の標準偏差をσ(r)(m)とする
とき、前記放出点と他の検出手段とを結ぶ直線のうち、
前記第1の検出手段に隣接する直線と放出点と前記第1
の検出手段を結ぶ直線がなす角度をθとする時、角度θ
が2sin-1{σ(r)/r}以内、もしくは2sin-1{3σ
(r)/2r}以内であることを特徴とする環境監視装
置。ここで、σ(r)の範囲は次式で与えられる。 0.05r0.8≦σ(r)≦0.3r0.92 2. An environment monitoring apparatus in which detection means for detecting the concentration of a substance released into the environment is disposed in the environment, wherein the distance from the release point to the first detection means is represented by r (m) and distance r. When the standard deviation of the diffusion width of the emission material is σ (r) (m), among the straight lines connecting the emission point and other detection means,
A straight line adjacent to the first detection means, an emission point, and the first
When the angle formed by the straight line connecting the detecting means is θ, the angle θ
Is within 2 sin -1 {σ (r) / r}, or 2 sin -1 {3σ
An environment monitoring device characterized by being within (r) / 2r}. Here, the range of σ (r) is given by the following equation. 0.05r 0.8 ≦ σ (r) ≦ 0.3r 0.92
検出手段を環境中に配置した環境監視装置において、放
出点から第1の検出手段までの距離をr(m),距離rに
おける放出物質の拡散幅の標準偏差をσ(r)(m)とする
とき、前記放出点と他の検出手段とを結ぶ直線上の放出
点からの距離rの点のうち、前記放出点と第1の検出手
段がなす直線に隣接する直線上にある点と、前記第1の
検出手段間の距離を4σ(r)以内もしくは6σ(r)以内
とすることを特徴とする環境監視装置。ここで、σ(r)
の範囲は次式で与えられる。 0.05r0.8≦σ(r)≦0.3r0.92 3. An environment monitoring apparatus in which a detecting means for detecting the concentration of a substance released into the environment is disposed in the environment, wherein a distance from the emission point to the first detecting means is represented by r (m) and a distance r. When the standard deviation of the diffusion width of the emission material is σ (r) (m), among the points at a distance r from the emission point on a straight line connecting the emission point and other detection means, the emission point and the second An environment monitoring device, wherein a distance between a point on a straight line adjacent to a straight line formed by the first detecting means and the first detecting means is within 4σ (r) or within 6σ (r). Where σ (r)
Is given by the following equation. 0.05r 0.8 ≦ σ (r) ≦ 0.3r 0.92
検出手段を環境中に配置した環境監視装置において、放
出点から第1の検出手段までの距離をr(m),距離rに
おける放出物質の拡散幅の標準偏差をσ(r)(m)とする
とき、前記放出点と他の検出手段とを結ぶ直線のうち、
前記第1の検出手段に隣接する直線と放出点と前記第1
の検出手段を結ぶ直線がなす角度θとする時、角度θが
2sin-1{2σ(r)/r}以内、もしくは2sin-1{3σ
(r)/r}以内であることを特徴とする環境監視装置。
ここで、σ(r)の範囲は次式で与えられる。 0.05r0.8≦σ(r)≦0.3r0.92 4. An environment monitoring apparatus in which detection means for detecting the concentration of a substance released into the environment is disposed in the environment, wherein the distance from the release point to the first detection means is represented by r (m) and distance r. When the standard deviation of the diffusion width of the emission material is σ (r) (m), among the straight lines connecting the emission point and other detection means,
A straight line adjacent to the first detection means, an emission point, and the first
When the angle θ is formed by a straight line connecting the detection means, the angle θ is within 2 sin −1 {2σ (r) / r} or 2 sin −1 {3σ
An environment monitoring device characterized by being within (r) / r}.
Here, the range of σ (r) is given by the following equation. 0.05r 0.8 ≦ σ (r) ≦ 0.3r 0.92
いて、前記検出手段の配置される位置が環境中に固定さ
れていることを特徴とする環境監視装置。5. An environment monitoring apparatus according to claim 1, wherein a position where said detection means is arranged is fixed in an environment.
いて、前記検出手段がその位置を環境中に固定された固
定検出手段と、環境中を移動可能な移動検出手段より構
成されていることを特徴とする環境監視装置。6. The apparatus according to claim 1, wherein said detecting means comprises a fixed detecting means whose position is fixed in an environment, and a moving detecting means movable in the environment. An environmental monitoring device characterized in that:
観測手段と拡散予測手段により環境中へ放出された物質
の拡散範囲を予測し、移動検出手段へ放出された物質の
拡散範囲と移動位置を指示,表示することを特徴とする
環境監視装置。7. The diffusion range of a substance released into the environment is predicted by weather forecasting means and diffusion prediction means or the weather observation means and diffusion prediction means, and the diffusion range and movement position of the substance released to the movement detection means. An environmental monitoring device characterized by indicating and displaying information.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9276862A JPH11118701A (en) | 1997-10-09 | 1997-10-09 | Environmental monitoring device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9276862A JPH11118701A (en) | 1997-10-09 | 1997-10-09 | Environmental monitoring device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH11118701A true JPH11118701A (en) | 1999-04-30 |
Family
ID=17575458
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9276862A Pending JPH11118701A (en) | 1997-10-09 | 1997-10-09 | Environmental monitoring device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH11118701A (en) |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2006133121A (en) * | 2004-11-08 | 2006-05-25 | Daikin Ind Ltd | Base, air pollution information providing system, air pollution prediction method, and ventilation device |
| US7523638B2 (en) * | 2003-08-20 | 2009-04-28 | Dennis Scott Prince | Innovative gas monitoring with spacial and temporal analysis |
| JP2010266304A (en) * | 2009-05-14 | 2010-11-25 | Genden Information System Co Ltd | System and method for monitoring of environmental radiation in emergency |
| US8510059B2 (en) | 2009-04-14 | 2013-08-13 | Airdar Inc. | Method and system for measuring emission and quantifying emission source |
| JP2013175054A (en) * | 2012-02-24 | 2013-09-05 | Toshiba Corp | Density distribution analysis device and density distribution analysis method |
| JP2014145747A (en) * | 2013-01-30 | 2014-08-14 | Toshiba Corp | Diffusion source estimation method and diffusion source estimation device |
| US8949037B2 (en) | 2003-08-20 | 2015-02-03 | Airdar Inc. | Method and system for detecting and monitoring emissions |
| CN109298135A (en) * | 2018-09-04 | 2019-02-01 | 中国科学院大气物理研究所 | An unmanned vehicle system for all-round environmental monitoring |
| JP2021189938A (en) * | 2020-06-03 | 2021-12-13 | 凸版印刷株式会社 | Measurement data collection system and measurement data collection method |
-
1997
- 1997-10-09 JP JP9276862A patent/JPH11118701A/en active Pending
Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7523638B2 (en) * | 2003-08-20 | 2009-04-28 | Dennis Scott Prince | Innovative gas monitoring with spacial and temporal analysis |
| US7743643B2 (en) | 2003-08-20 | 2010-06-29 | Airdar Inc. | Innovative gas monitoring with spacial and temporal analysis |
| US7934412B2 (en) | 2003-08-20 | 2011-05-03 | Airdar Inc. | Innovative gas monitoring with spacial and temporal analysis |
| US8949037B2 (en) | 2003-08-20 | 2015-02-03 | Airdar Inc. | Method and system for detecting and monitoring emissions |
| JP2006133121A (en) * | 2004-11-08 | 2006-05-25 | Daikin Ind Ltd | Base, air pollution information providing system, air pollution prediction method, and ventilation device |
| US8510059B2 (en) | 2009-04-14 | 2013-08-13 | Airdar Inc. | Method and system for measuring emission and quantifying emission source |
| JP2010266304A (en) * | 2009-05-14 | 2010-11-25 | Genden Information System Co Ltd | System and method for monitoring of environmental radiation in emergency |
| JP2013175054A (en) * | 2012-02-24 | 2013-09-05 | Toshiba Corp | Density distribution analysis device and density distribution analysis method |
| JP2014145747A (en) * | 2013-01-30 | 2014-08-14 | Toshiba Corp | Diffusion source estimation method and diffusion source estimation device |
| CN109298135A (en) * | 2018-09-04 | 2019-02-01 | 中国科学院大气物理研究所 | An unmanned vehicle system for all-round environmental monitoring |
| CN109298135B (en) * | 2018-09-04 | 2024-01-30 | 中国科学院大气物理研究所 | Unmanned vehicle system for omnibearing environment monitoring |
| JP2021189938A (en) * | 2020-06-03 | 2021-12-13 | 凸版印刷株式会社 | Measurement data collection system and measurement data collection method |
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