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JPH0737974B2 - Organic carbon measuring device - Google Patents
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JPH0737974B2 - Organic carbon measuring device - Google Patents

Organic carbon measuring device

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Publication number
JPH0737974B2
JPH0737974B2 JP63044820A JP4482088A JPH0737974B2 JP H0737974 B2 JPH0737974 B2 JP H0737974B2 JP 63044820 A JP63044820 A JP 63044820A JP 4482088 A JP4482088 A JP 4482088A JP H0737974 B2 JPH0737974 B2 JP H0737974B2
Authority
JP
Japan
Prior art keywords
carbon
acid
inorganic
carbon dioxide
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.)
Expired - Lifetime
Application number
JP63044820A
Other languages
Japanese (ja)
Other versions
JPH01219559A (en
Inventor
洋造 森田
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
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Filing date
Publication date
Application filed by Shimadzu Corp filed Critical Shimadzu Corp
Priority to JP63044820A priority Critical patent/JPH0737974B2/en
Publication of JPH01219559A publication Critical patent/JPH01219559A/en
Publication of JPH0737974B2 publication Critical patent/JPH0737974B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、産業廃水、湖沼水、海水、河川水等に含まれ
る全有機炭素を測定する有機炭素測定装置に関し、特に
全有機炭素が微少量であってもこれを高精度に測定する
ことのできる有機炭素測定装置に関する。
Description: TECHNICAL FIELD The present invention relates to an organic carbon measuring device for measuring total organic carbon contained in industrial wastewater, lake water, seawater, river water, etc. The present invention relates to an organic carbon measuring device that can measure even a small amount with high accuracy.

〔従来の技術〕[Conventional technology]

従来のこの種の装置は、試料水に含まれる全炭素を二酸
化炭素に変換し、この二酸化炭素を定量することによっ
て試料水中の全炭素を求め、次いで上記の試料水に含ま
れる無機炭素を二酸化炭素に変換し、この二酸化炭素を
同様に定量して無機炭素を求め、両者の差から有機炭素
を求めるようにしている。
Conventional devices of this type convert total carbon contained in sample water into carbon dioxide, determine the total carbon in the sample water by quantifying the carbon dioxide, and then convert the inorganic carbon contained in the sample water to carbon dioxide. It is converted into carbon, and this carbon dioxide is similarly quantified to obtain inorganic carbon, and the organic carbon is obtained from the difference between the two.

全炭素を二酸化炭素に変換するには、燃焼炉が用いられ
ている。この燃焼炉には、例えば白金触媒等の触媒が充
填されており、燃焼炉に一定量注入した試料水をキャリ
アガスとともに所定の空間速度で650〜950℃に昇温した
充填層を通過させることによって全炭素のうち、有機炭
素は燃焼させて二酸化炭素に変換し、無機炭素である炭
素塩、炭酸水素塩は熱分解して二酸化炭素に変換するよ
うにしていた。燃焼生成物の中には二酸化炭素の他に水
蒸気が含まれているが、これは、燃焼炉のあとに取付け
られたドレンセパレータによって凝集除去するようにし
ていた。
Combustion furnaces are used to convert all carbon to carbon dioxide. This combustion furnace is filled with a catalyst such as a platinum catalyst, and a certain amount of sample water injected into the combustion furnace is allowed to pass through a packed bed heated to 650 to 950 ° C at a predetermined space velocity together with a carrier gas. Thus, among all the carbon, organic carbon is burned to be converted into carbon dioxide, and carbon salts and hydrogen carbonates which are inorganic carbon are thermally decomposed and converted into carbon dioxide. In addition to carbon dioxide, water vapor was contained in the combustion products, and this was coagulated and removed by a drain separator attached after the combustion furnace.

一方、無機炭素を二酸化炭素に変換するには、反応炉が
用いられている。反応炉としては例えば特公昭52−2036
0号公報記載のものがある。この種の反応炉には、内部
に燐酸を被覆させた石英ガラス粒担体等が充填されてお
り、この燐酸と無機炭素である炭酸塩、炭酸水素塩とを
150℃前後で反応(例えばNa2CO3+H3PO4→Na2HPO4+CO2
+H2O)させて二酸化炭素に変換するようにしていた。
On the other hand, a reaction furnace is used to convert inorganic carbon into carbon dioxide. As a reactor, for example, Japanese Patent Publication No. Sho 52-2036
There is one disclosed in Japanese Patent No. 0. This type of reaction furnace is filled with a quartz glass particle carrier or the like coated with phosphoric acid, and the phosphoric acid and the inorganic carbon carbonate or hydrogencarbonate are charged.
Reaction around 150 ℃ (eg Na 2 CO 3 + H 3 PO 4 → Na 2 HPO 4 + CO 2
+ H 2 O) to convert to carbon dioxide.

このようにして生成した各二酸化酸素は、それぞれ反応
炉の下流側に接続されたガス検出部、例えば非分散形赤
外線ガス分析計に流入し、赤外線分析に付され、得られ
た二酸化炭素濃度に対応したピーク信号のピーク高さあ
るいはピーク面積を求めることによって定量するように
していた。二酸化炭素が定量されると、予め用意された
全炭素の標準液から求められた、二酸化炭素のピーク高
さあるいはピーク面積と全炭素濃度の関係(一次式)の
グラフから、今定量された二酸化炭素に基づく試料中の
全炭素濃度が求められる。
Each oxygen dioxide generated in this way, flows into a gas detection unit connected to the downstream side of the reaction furnace, for example, a non-dispersion type infrared gas analyzer, is subjected to infrared analysis, and has a carbon dioxide concentration obtained. Quantification was performed by obtaining the peak height or peak area of the corresponding peak signal. When carbon dioxide is quantified, the quantified carbon dioxide is determined from the graph of the relationship between carbon dioxide peak height or peak area and total carbon concentration (linear equation), which was obtained from the prepared standard solution of total carbon. The total carbon concentration in the carbon-based sample is determined.

上述の如く従来の有機炭素測定装置は、キャリアガスを
供給するキャリアガス供給部、燃焼炉、反応炉及びガス
検出部により構成され、これらはキャリアガスの上流部
から下流部へと順次連通管によって直列に接続されてい
る。用いられるキャリアガスとしては実質的に二酸化炭
素を含まないもので、例えば高純度に精製された空気や
窒素等がよく用いられる。
As described above, the conventional organic carbon measuring device is composed of a carrier gas supply unit for supplying a carrier gas, a combustion furnace, a reaction furnace, and a gas detection unit, which are sequentially connected from the upstream portion to the downstream portion of the carrier gas by a communication pipe. It is connected in series. The carrier gas used does not substantially contain carbon dioxide, and, for example, highly purified air or nitrogen is often used.

〔発明が解決しようとする課題〕[Problems to be Solved by the Invention]

従来の有機炭素測定装置は、産業廃水、湖沼水等に含ま
れる有機炭素を測定するには確かに有力なものではある
が、現実に採取する試料水には有機物・無機物が多種多
様に含まれており、燃焼生成ガス中には腐食成分等が含
まれ、あるいは反応炉での反応に障害になる成分等も含
まれていることがあるなどして、いくつかの課題が残さ
れていた。
Although conventional organic carbon analyzers are certainly effective in measuring organic carbon contained in industrial wastewater, lake water, etc., the sample water actually collected contains a wide variety of organic and inorganic substances. However, some of the problems remain, since the combustion product gas may contain a corrosive component or the like, or a component that interferes with the reaction in the reaction furnace.

つまり、酸、塩類を多く含む試料水には、燃焼炉におい
て塩酸、硝酸などの腐食成分を生成し、これらが確実に
除去されないとガス検出部の測定用セルを腐食して測定
誤差をもたらすとともに、二酸化炭素の吸収スペクトル
と干渉するスペクトルを生成し、二酸化炭素の測定に誤
差を与えることになる。
That is, corrosive components such as hydrochloric acid and nitric acid are generated in the sample water containing a large amount of acids and salts in the combustion furnace, and if these are not removed reliably, they will corrode the measurement cell of the gas detection unit and cause measurement errors. However, it produces a spectrum that interferes with the absorption spectrum of carbon dioxide, which gives an error in the measurement of carbon dioxide.

また、無機炭素を測定する反応炉は、150℃前後に昇温
して用いられるため、シュウ酸、リンゴ酸などの低級カ
ルボン酸の中の易酸化性成分を含む試料では、これらが
容易に熱分解し、二酸化炭素を生成して無機炭素の定量
値に誤差を生じさせる原因になっていた。
In addition, since the reaction furnace for measuring inorganic carbon is used by raising the temperature to around 150 ° C, it can be easily heated in samples containing easily oxidizable components in lower carboxylic acids such as oxalic acid and malic acid. It decomposed and produced carbon dioxide, which caused an error in the quantitative value of inorganic carbon.

さらに、反応炉が150℃前後に昇温されているため、例
えば海水などのように塩化ナトリウムなどの塩類を多く
含む試料では、反応体である燐酸と反応(NaCl+H3PO4
→NaH2PO4+HCl)して、酸を発生し、上述したと同様、
腐食、測定誤差を招いていた。
Furthermore, since the temperature of the reactor is raised to around 150 ° C, samples such as seawater that contain a large amount of salts such as sodium chloride react with phosphoric acid (NaCl + H 3 PO 4
→ NaH 2 PO 4 + HCl) to generate an acid, similar to the above
It caused corrosion and measurement error.

また、無機炭素を微量にしか含まない試料で、これを正
確に測定しようとする場合、止むを得ず多量の試料を用
いなければならない。ところが従来の反応炉では、多量
の試料、例えば200μ以上の試料を注入すると充填層
の燐酸などが試料中に流出したり、充填層の温度低下を
もたらし、これらのことによってガス検出部で得られる
二酸化炭素のピーク信号テーリングが著しく、正確な測
定が困難であり、試料の注入量は200μが限度であっ
た。
Further, in order to accurately measure a sample containing only a small amount of inorganic carbon, a large amount of sample must be used. However, in a conventional reaction furnace, when a large amount of sample, for example, 200 μm or more, is injected, phosphoric acid in the packed bed flows out into the sample and causes a decrease in the temperature of the packed bed. The peak signal tailing of carbon dioxide was remarkable and accurate measurement was difficult, and the injection volume of the sample was limited to 200μ.

本発明は上記課題を解決するためになされたもので、試
料水中に酸、塩類を多く含むものであっても、また試料
水中の無機炭素が微少量しか含まれないものであって
も、高精度に無機炭素を測定することのできる有機炭素
測定装置を提供することを目的としている。
The present invention has been made to solve the above problems, even if the sample water contains a large amount of acid and salts, and even if the sample water contains only a small amount of inorganic carbon, It is an object of the present invention to provide an organic carbon measuring device capable of accurately measuring inorganic carbon.

〔課題を解決するための手段〕[Means for Solving the Problems]

本発明に係る有機炭素測定装置は、試料水を注入して有
機炭素及び無機炭素を燃焼または熱分解させてこれらの
全炭素を二酸化炭素に変換する燃焼部と、上記試料水を
注入して無機炭素を反応させて二酸化炭素に変換する反
応部と、上記各二酸化炭素をそれぞれ個別に検出して定
量し、上記全炭素及び無機炭素を算出し全炭素と無機炭
素との差から有機炭素を測定する有機炭素測定装置にお
いて、上記燃焼部には捕集液を収容した捕集部を連結
し、該燃焼部からの燃焼生成ガスをバブリングさせて該
燃焼生成ガスを浄化するべく構成し、かつ上記捕集部に
は試料水の注入口を設けて適時酸とともに該試料水を該
注入口を介して注入し、酸性水溶液中において無機炭素
を二酸化炭素に変換する反応部として上記捕集部を構成
したものである。
The organic carbon measuring device according to the present invention comprises a combustion unit for injecting sample water to combust or thermally decompose organic carbon and inorganic carbon to convert all of these carbons into carbon dioxide, and inject the sample water for inorganic treatment. A reaction part for reacting carbon to convert it to carbon dioxide and each of the carbon dioxides are individually detected and quantified, and the total carbon and the inorganic carbon are calculated, and the organic carbon is measured from the difference between the total carbon and the inorganic carbon. In the organic carbon measuring device according to the above, the combustion part is connected to a collection part containing a collection liquid, and the combustion product gas from the combustion part is bubbled to purify the combustion product gas. The collection part is provided with a sample water injection port, and the sample water is injected through the injection port together with an acid at appropriate times, and the collection part is configured as a reaction part for converting inorganic carbon into carbon dioxide in an acidic aqueous solution. It was done.

なお、同様の目的で上記捕集部には捕集液の代りに固体
酸を収容することもできる。
For the same purpose, a solid acid may be stored in the collection part instead of the collection liquid.

〔作用〕[Action]

本発明によれば、全炭素を測定する場合には燃焼部に試
料を注入すると全炭素は二酸化炭素に変換されて他の水
蒸気等とともに捕集部でバブリングし、二酸化炭素のみ
がギャリアガスとともに検出部に達して、二酸化炭素が
定量され、無機炭素を測定する場合には捕集部の注入口
から適時酸とともに試料を注入すると捕集液中で分解し
て二酸化炭素に変換されて検出部に達し、二酸化炭素の
定量がされ、前者(全炭素)から校舎(無機炭素)を差
し引くことにより有機炭素を測定することができる。
According to the present invention, when measuring a total carbon, when a sample is injected into the combustion section, the total carbon is converted into carbon dioxide and bubbled in the collection section together with other water vapor etc., and only carbon dioxide is detected along with the gallery gas in the detection section. When the amount of carbon dioxide is quantified, and when measuring inorganic carbon, the sample is injected with the acid from the inlet of the collection part in a timely manner, it is decomposed in the collection liquid and converted into carbon dioxide and reaches the detection part. , The amount of carbon dioxide is quantified, and the organic carbon can be measured by subtracting the school building (inorganic carbon) from the former (total carbon).

なお、捕集部に固体酸を収容した場合にあっては、この
固体酸が試料中の炭酸水素塩等のカチオンイオンとイオ
ン交換し、この時生成した炭酸をキャリアガスでバブリ
ングすれば容易に二酸化炭素に変換する。また、この固
体酸は燃焼生成ガス中の酸類によって容易に再生され
る。
When the solid acid is stored in the collection unit, this solid acid is ion-exchanged with cation ions such as hydrogen carbonate in the sample, and the carbon dioxide generated at this time can be easily bubbled with a carrier gas. Convert to carbon dioxide. Moreover, this solid acid is easily regenerated by the acids in the combustion product gas.

〔実施例〕〔Example〕

以下図示実施例に基づいて本発明を説明する。 The present invention will be described below based on illustrated embodiments.

第1図は本実施例装置の構成を示す概略図である。同図
に示すように、有機炭素測定装置は、キャリアガスを供
給するキャリアガス供給部(1)と、キャリアガス供給
部(1)に対し配管(2)を介して連通された燃焼炉
(3)と、燃焼炉(3)に対し接続管(4)を介して連
通された捕集部(5)と、捕集部(5)に対し配管
(6)を介して連通され二酸化炭素を検出するガス検出
部(7)と、二酸化炭素の検出部(7)の検出結果をグ
ラフとして記録する記録部(8)とを備えて構成されて
いる。更に捕集部(5)と検出部(7)とを継ぐ配管
(6)は同図示の如く途中にU字管部(6a)を形成する
とともに、この配管(6)を流通するガスはこれを冷却
し除湿する除湿部(9)を経由することにより水分が凝
縮され、この凝縮水はトラップ(10)に捕集するように
なされている。また除湿部(9)と検出部(7)との間
の配管(6)にはフィルタ(11)が取付けられており、
検出部(7)に流入するガスを清浄化するようになされ
ている。
FIG. 1 is a schematic diagram showing the configuration of the apparatus of this embodiment. As shown in the figure, the organic carbon measuring apparatus includes a carrier gas supply unit (1) for supplying a carrier gas and a combustion furnace (3) connected to the carrier gas supply unit (1) through a pipe (2). ), A collection part (5) communicated with the combustion furnace (3) through a connecting pipe (4), and a collection part (5) communicated with the collection part (5) through a pipe (6) to detect carbon dioxide. And a recording unit (8) for recording the detection result of the carbon dioxide detection unit (7) as a graph. Further, the pipe (6) connecting the collection part (5) and the detection part (7) forms a U-shaped pipe part (6a) in the middle as shown in the figure, and the gas flowing through this pipe (6) is The water is condensed by passing through a dehumidifying section (9) for cooling and dehumidifying the condensed water, and the condensed water is collected in the trap (10). A filter (11) is attached to the pipe (6) between the dehumidifying section (9) and the detecting section (7),
The gas flowing into the detector (7) is cleaned.

然して本実施例装置の特徴は、上述の如く燃焼炉(3)
に捕集部(5)を直接連結し、かつこの捕集部(5)を
上述した反応部として構成した点にある。即ち、この捕
集部(5)には一定量の捕集液(12)が収容されてお
り、燃焼炉(3)からの燃焼生成ガスをキャリアガスと
ともに捕集部(5)下端から捕集液に直接バブリングさ
せるように構成されている。従ってマイクロシリンジ
(12)によって燃焼炉(3)に注入する試料水が酸、塩
類を多く含み、この燃焼炉(3)で腐食成分あるいはガ
ス検出部(7)における干渉成分を生成しても、捕集部
(5)の捕集液(12)中をこの燃焼生成ガスがバブリン
グする間にこれらの成分は捕集液(12)に捕獲、除去さ
れる。捕集液としては水を用いるが、これは燃焼炉から
の燃焼生成ガスに含まれる水分が凝集したドレンとし
て、次々と補給されるため、通常、外部から加える必要
はない。一般に試料水中に酸や塩分が含まれることが多
いが、これらの燃焼生成物を水に溶解させると、塩化物
からは塩酸、硝酸塩からは硝酸、亜硝酸、硫酸塩からは
硫酸、亜硫酸などの鉱酸を生成するため、酸性になる
が、これが次に述べる無機炭素を測定するための反応液
として役立つことになる。
However, the feature of the apparatus of this embodiment is that the combustion furnace (3) is as described above.
The collecting part (5) is directly connected to the above, and this collecting part (5) is configured as the above-mentioned reaction part. That is, a fixed amount of the collected liquid (12) is contained in the collection part (5), and the combustion product gas from the combustion furnace (3) is collected together with the carrier gas from the lower end of the collection part (5). It is configured to directly bubble the liquid. Therefore, even if the sample water injected into the combustion furnace (3) by the microsyringe (12) contains a large amount of acid and salts, and a corrosion component or an interference component in the gas detection section (7) is generated in this combustion furnace (3), These components are captured and removed by the collection liquid (12) while the combustion product gas is bubbled through the collection liquid (12) of the collection unit (5). Although water is used as the collected liquid, it is not necessary to add it from the outside because it is supplied one after another as drainage in which water contained in the combustion product gas from the combustion furnace is condensed. In general, acid and salt are often contained in sample water, but when these combustion products are dissolved in water, hydrochloric acid from chloride, nitric acid from nitrate, nitrous acid, sulfuric acid from sulfuric acid, sulfurous acid, etc. It produces a mineral acid, which makes it acidic, which serves as a reaction solution for measuring inorganic carbon as described below.

更に、この捕集部(5)は、上述の如く無機炭素の反応
炉としての作用をも併せもっている。即ち、捕集部
(5)は試料を注入する注入口(図示せず)を有し、従
来の反応炉と同様にこの注入口からマイクロシリンジ
(13)などによって試料を注入することができるように
構成されている。そして本実施例では、無機炭素である
解離した炭酸イオン、炭酸水素イオンの分解を促進する
ために、試料を注入する際、例えば試料注入前、あるい
はほぼ同時、あるいは注入直後の適時に、塩酸、硝酸、
燐酸、硫酸などの酸を併せて注入する。酸としては無機
酸が用いられ、特に塩酸が好ましい。通常、捕集液のPH
が3以下であると上記分解は確実なものとなることを確
認している。この酸の注入は試料注入毎に行なう必要は
なく、例えば2N−HClを0.5ml注入すれば10回程度の試料
測定は可能である。さらに、上記したように、燃焼炉か
らの燃焼生成物が捕集部内の捕集液に溶解すると、試料
中の酸や塩分から鉱酸を生成するため、通常、この捕集
液は、酸を添加しなくても、ほとんどの場合、PH3以下
の強酸性になっている。つまり、本実施例では従来排出
していた酸類を有効に利用していることになる。
Further, the collecting section (5) also has a function as a reaction furnace for inorganic carbon as described above. That is, the collection unit (5) has an injection port (not shown) for injecting the sample, and the sample can be injected from this injection port by a microsyringe (13) or the like like a conventional reaction furnace. Is configured. In this embodiment, in order to accelerate the decomposition of dissociated carbonate ions, which are inorganic carbon, and hydrogen carbonate ions, hydrochloric acid, when injecting a sample, for example, before sample injection, or almost at the same time, or immediately after injection, nitric acid,
An acid such as phosphoric acid or sulfuric acid is also injected. An inorganic acid is used as the acid, and hydrochloric acid is particularly preferable. Usually, PH of the collected liquid
It has been confirmed that the above decomposition becomes reliable when the value is 3 or less. It is not necessary to inject this acid every time the sample is injected, and for example, if 0.5 ml of 2N-HCl is injected, the sample can be measured about 10 times. Further, as described above, when the combustion product from the combustion furnace is dissolved in the trapping liquid in the trapping portion, mineral acid is generated from the acid or salt in the sample. In most cases, even if it is not added, it has a strong acidity of PH3 or less. That is, in the present example, the acids that were conventionally discharged are effectively used.

また、捕集部(5)は室温で用いられ、従来の如く加熱
はしない。従って無機炭素の測定の際、試料中に易酸化
性の低級カルボン酸が含まれていてもこれら低級カルボ
ン酸は熱分解して二酸化炭素を生成することがなく、ひ
いては無機炭素の測定誤差要因とならず、測定精度の向
上を図ることができる。
Further, the collecting part (5) is used at room temperature and is not heated unlike the conventional case. Therefore, when measuring inorganic carbon, even if the sample contains easily oxidizable lower carboxylic acids, these lower carboxylic acids do not pyrolyze to generate carbon dioxide, and as a result, they may cause an error in measuring inorganic carbon. Therefore, the measurement accuracy can be improved.

また、捕集部(5)は、従来の如く塩化ナトリウムなど
の塩分を含む試料であっても加熱していないため内部で
反応して塩酸などの酸蒸気を発生することもなく、従っ
て誤差なく無機炭素を測定することができる。更に従来
の如く燐酸などを担体に担持させたものでないことか
ら、従来より可成り多くの試料を注入することができ、
試料中の無機炭素が微少量であっても注入量を増すこと
によって無機炭素を正確に測定することができる。従っ
て、従来200μの注入量が限度であったものが、本実
施例では略10倍以上の試料を用いることができ、従来の
1/10以下の濃度であっても測定することができる(即ち
測定感度が10倍以上になる)ことが確認されている。
Further, since the collecting section (5) does not heat even a sample containing salt such as sodium chloride as in the conventional case, it does not react to generate an acid vapor such as hydrochloric acid inside the sample, so that there is no error. Inorganic carbon can be measured. Furthermore, unlike the conventional method, phosphoric acid or the like is not supported on the carrier, so that a considerably larger number of samples can be injected than the conventional method.
Inorganic carbon can be accurately measured by increasing the injection amount even if the amount of inorganic carbon in the sample is very small. Therefore, although the conventional injection amount of 200μ was the limit, in the present embodiment, a sample of about 10 times or more can be used.
It has been confirmed that measurement can be performed even at a concentration of 1/10 or less (that is, the measurement sensitivity is 10 times or more).

さらに、捕集部(5)には捕集液を一定量に保つために
排出用の弁(5a)が取付けられている(同図参照)。ま
た捕集液(12)のPHを管理するためのPH計(5b)も取付
けることができる。尚、排出用の弁(5a)は自動弁と
し、これにコントローラを付設することにより、コント
ローラの信号によって測定に先立ち過剰ドレンを排出す
るようにもできる。
Further, a discharge valve (5a) is attached to the collection part (5) in order to keep the collected liquid at a constant amount (see the same figure). A PH meter (5b) for controlling the PH of the collected liquid (12) can also be attached. The discharge valve (5a) is an automatic valve, and by attaching a controller thereto, excess drain can be discharged prior to measurement by a signal from the controller.

尚、捕集部(5)はガラスあるいはプラスチックなどの
容器によって構成され、下部には図示の如く捕集液収容
部(5c)が形成され、その直径は10〜15mmの範囲で、長
さが20〜50mmの範囲が好ましく、1〜10mlの捕集液(1
2)が常時滞留しているように液面を管理すると良く、
さらにバブリングの際に発生する気泡の飛散を防止する
ために捕集部(5)に、断面積大きくするために図のよ
うな直径20〜30mmの球状をなす泡切り部(5d)を設けて
おくと良い。
The collection part (5) is composed of a container such as glass or plastic, and a collection liquid storage part (5c) is formed in the lower part as shown in the drawing, and its diameter is in the range of 10 to 15 mm and the length is The range of 20 to 50 mm is preferable, and 1 to 10 ml of the collection liquid (1
It is good to manage the liquid level so that 2) stays at all times,
In addition, in order to prevent the scattering of bubbles generated during bubbling, the collection part (5) is provided with a spherical bubble cutting part (5d) with a diameter of 20 to 30 mm as shown in the figure to increase the cross-sectional area. It is good to leave.

また、有機炭素を測定する場合には、燃焼炉(3)の燃
焼生成ガスを捕集部(5)の捕集液(12)で洗浄するた
めに、洗浄力に必要な一定量の捕集液(12)を確保して
おく必要がある。一定量を超える場合には上述した排出
用の弁(5a)を開放して一定量にする。尚、測定開始時
には予め標準液を数回通し、キャリブレーションを行な
うことから、その時に発生した燃焼生成ガス中の水分が
凝集したドレンが捕集部に集まり、これが捕集液として
はたらくため試料測定時には捕集液(12)は一定量確保
されていることが多い。
In addition, when measuring organic carbon, a certain amount of trapping required for detergency is required in order to wash the combustion product gas of the combustion furnace (3) with the trapping liquid (12) of the trapping part (5). It is necessary to reserve the liquid (12). When the amount exceeds a certain amount, the discharge valve (5a) described above is opened to a constant amount. Since the standard solution is passed through the calibration solution several times in advance at the start of the measurement, the drainage from which the water in the combustion product gas generated at that time agglomerates collects in the collection part and acts as a collection solution. Sometimes, a fixed amount of the collected liquid (12) is secured.

尚、試料の注入手段として、シリンジポンプを用いて自
動注入方式を採用することができ、この自動注入方式の
場合には、シリンジポンプを酸の注入手段としても用い
ることができ、予めこのシリンジポンプに酸を一定量注
入しておけば自動的に必要量の酸を捕集部(5)に注入
することができる。
As a sample injection means, a syringe pump can be used as an automatic injection method. In the case of this automatic injection method, the syringe pump can also be used as an acid injection means. By injecting a certain amount of acid into, the required amount of acid can be automatically injected into the collection unit (5).

尚、本実施例装置における上記以外の構成は従来装置と
同様に構成することができるためにその説明は省略し
た。
Since the configuration of the apparatus of this embodiment other than the above can be configured in the same manner as the conventional apparatus, the description thereof is omitted.

次に本発明の他の実施例について説明する。本実施例で
は、捕集部(5)に予め固体酸としての強酸性イオン交
換樹脂(H型)(たとえば「アンバーライトIR−120B」
(米国のローム・アンド・ハース社の登録商標),オル
ガノ株式会社製)を収容した点に特徴を有し、他は上記
実施例と同様に構成されている。
Next, another embodiment of the present invention will be described. In this example, a strongly acidic ion exchange resin (H type) as a solid acid (for example, "Amberlite IR-120B") was previously collected in the collection section (5).
(Registered trademark of Rohm and Haas Company in the United States, manufactured by Organo Co., Ltd.) is featured, and the other configurations are similar to those of the above-described embodiment.

強酸性イオン交換樹脂を収容しておくと、これが試料中
の炭酸水素塩等のカチオンとイオン交換(例えばR−SO
3H+NaHCO3→R−SO3Na+H2CO3)し、この時生成した生
成物、つまり炭酸をキャリアガスによってバブリングす
れば容易に二酸化炭素に変換され(H2CO3→H2O+C
O2)、上記実施例と同様の作用効果を奏し得る。
When a strongly acidic ion exchange resin is stored, it exchanges ions with cations such as hydrogen carbonate in the sample (for example, R-SO.
3 H + NaHCO 3 → R-SO 3 Na + H 2 CO 3 ), and the product generated at this time, that is, carbonic acid, is bubbled by a carrier gas, so that it is easily converted into carbon dioxide (H 2 CO 3 → H 2 O + C
O 2 ), and the same effects as those of the above embodiment can be obtained.

強酸性イオン交換樹脂の収容方法としては、例えばこの
強酸性イオン交換樹脂を50メッシュの白金金網に2ml収
容し、収容した状態のまま捕集部(5)に入れ、捕集液
を一定量満たしておけば良い。
As a method for accommodating the strongly acidic ion-exchange resin, for example, 2 ml of this strongly acidic ion-exchange resin is accommodated in a 50-mesh platinum wire mesh, and the accommodating solution (5) is placed in the accommodating state, and a certain amount of the collecting liquid is filled. You can leave it.

この場合、イオン交換反応によって強酸性イオン交換樹
脂の交換能力が低下しても、燃焼生成ガス中の種類によ
って容易に再生(例えばR−SO3Na+HCl→R−SO3H+Na
Cl)されるからこのイオン交換樹脂を繰り返し使用する
ことができる。このように強酸性イオン交換樹脂を捕集
部(5)に収容することによって、上記実施例の如く、
無機炭素の測定時に酸性溶液を捕集部(5)に注入する
必要がなくなり、操作が更に簡便になる。尚、固体酸で
あれば上記反応を阻害しない限り強酸性イオン交換樹脂
以外のものであっても適宜用いることができる。
In this case, even if the reduced exchange capacity of a strongly acidic ion-exchange resin by the ion exchange reaction, easily regenerated by the type of the combustion product gas (e.g., R-SO 3 Na + HCl → R-SO 3 H + Na
This ion-exchange resin can be used repeatedly because it is Cl). By storing the strongly acidic ion exchange resin in the collection part (5) in this manner,
It is not necessary to inject the acidic solution into the collection part (5) at the time of measuring the inorganic carbon, and the operation becomes simpler. Any solid acid other than a strongly acidic ion exchange resin can be used as appropriate as long as it does not hinder the above reaction.

〔発明の効果〕〔The invention's effect〕

以上本発明によれば、試料中の酸、塩類を多く含むもの
であっても、また試料中の無機炭素が微少量であって
も、確実かつ高精度に無機炭素を測定することができ
る。
As described above, according to the present invention, it is possible to reliably and highly accurately measure inorganic carbon even if the sample contains a large amount of acid or salt, and even if the sample contains a very small amount of inorganic carbon.

なお、捕集部に固体酸を収容するようにすれば、この固
体酸がイオン交換反応を起こすことから、無機炭素の測
定時に酸性溶液を該捕集部に注入する必要がなくなり、
操作性がさらに向上する。
Incidentally, if the solid acid is accommodated in the collection part, since the solid acid causes an ion exchange reaction, it is not necessary to inject an acidic solution into the collection part at the time of measuring inorganic carbon,
Operability is further improved.

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

第1図は本発明に係る有機炭素測定装置の一実施例を示
す概略構成図である。 図において、 (5)は捕集部、 (12)は捕集液である。
FIG. 1 is a schematic configuration diagram showing an embodiment of the organic carbon measuring device according to the present invention. In the figure, (5) is a collection part and (12) is a collection liquid.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】試料水と注入して有機炭素及び無機炭素を
燃焼あるいは熱分解させてこれらの全炭素を二酸化炭素
に変換する燃焼部と、上記試料水を注入して無機炭素を
反応させて二酸化炭素に変換する反応部と、上記各二酸
化炭素をそれぞれ個別に検出して定量し、上記全炭素及
び無機炭素を算出して全炭素と無機炭素との差から有機
炭素を測定する有機炭素測定装置において、上記燃焼部
には捕集液を収容した捕集部を連結し、該燃焼部かの燃
焼生成ガスをバブリングさせて該燃焼生成ガスを浄化す
るべく構成し、かつ上記捕集部には試料水の注入口を設
けて適時酸とともに該試料水を該注入口を介して注入
し、酸性水溶液中において無機炭素を二酸化炭素に変換
する反応部として上記捕集部を構成したことを特徴とす
る有機炭素測定装置。
1. A combustion part for injecting sample water to combust or thermally decompose organic carbon and inorganic carbon to convert all of these carbons into carbon dioxide, and injecting the sample water for reacting inorganic carbon Organic carbon measurement to measure the organic carbon from the difference between the total carbon and the inorganic carbon by calculating the total carbon and the inorganic carbon by individually detecting and quantifying each of the carbon dioxide In the apparatus, a collecting unit containing a collected liquid is connected to the combustion unit, and the combustion product gas of the combustion unit is bubbled to purify the combustion product gas. Is characterized in that the sample water inlet is provided, and the sample water is injected with the acid at the appropriate time through the inlet, and the collecting portion is configured as a reaction portion for converting inorganic carbon into carbon dioxide in an acidic aqueous solution. Measuring device for organic carbon
JP63044820A 1988-02-26 1988-02-26 Organic carbon measuring device Expired - Lifetime JPH0737974B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63044820A JPH0737974B2 (en) 1988-02-26 1988-02-26 Organic carbon measuring device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63044820A JPH0737974B2 (en) 1988-02-26 1988-02-26 Organic carbon measuring device

Publications (2)

Publication Number Publication Date
JPH01219559A JPH01219559A (en) 1989-09-01
JPH0737974B2 true JPH0737974B2 (en) 1995-04-26

Family

ID=12702081

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63044820A Expired - Lifetime JPH0737974B2 (en) 1988-02-26 1988-02-26 Organic carbon measuring device

Country Status (1)

Country Link
JP (1) JPH0737974B2 (en)

Also Published As

Publication number Publication date
JPH01219559A (en) 1989-09-01

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