JPH0773512B2 - Quantitative method and quantification device for microorganisms - Google Patents
Quantitative method and quantification device for microorganismsInfo
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- JPH0773512B2 JPH0773512B2 JP3834188A JP3834188A JPH0773512B2 JP H0773512 B2 JPH0773512 B2 JP H0773512B2 JP 3834188 A JP3834188 A JP 3834188A JP 3834188 A JP3834188 A JP 3834188A JP H0773512 B2 JPH0773512 B2 JP H0773512B2
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Description
【発明の詳細な説明】 (イ)産業上の利用分野 この発明は、微生物等の定量法及び定量装置に関する。
さらに詳しくは、試料液中の微生物や発熱性物質を簡便
かつ信頼性良く定量しうる定量法及び定量装置に関す
る。TECHNICAL FIELD The present invention relates to a quantification method and quantification device for microorganisms and the like.
More specifically, the present invention relates to a quantification method and a quantification device that can easily and reliably quantify microorganisms and pyrogens in a sample solution.
(ロ)従来の技術 種々の媒体中の微生物量の測定(定量)は、発酵、醸造
等の微生物を積極的に利用する分野のみならず、医療、
食品、分析等の種々の分野で公衆衛生や品質管理上重要
である。(B) Conventional technology The measurement (quantification) of the amount of microorganisms in various media can be performed not only in fields such as fermentation and brewing where microorganisms are actively used, but also in medical treatment.
It is important for public health and quality control in various fields such as food and analysis.
かかる微生物の定量法として従来から以下のような方法
が一般的に知られている。The following methods have been generally known as methods for quantifying such microorganisms.
目視的計側法:微生物含有試料液を染色処理した後、
スライドグラス上に載せて顕微鏡で視野内の菌数をカウ
ントし、この値に基づいて微生物量を菌数として定量す
る方法など。Visual measurement method: After dyeing the sample solution containing microorganisms,
For example, a method of counting the number of bacteria in the visual field with a microscope placed on a slide glass and quantifying the amount of microorganisms as the number of bacteria based on this value.
光学的計側法:微生物含有試料液に光を照射してその
濁度を計測し、この値に基づいて微生物量を定量する方
法など。Optical metering method: A method of irradiating a sample solution containing microorganisms with light to measure the turbidity and quantifying the amount of microorganisms based on this value.
希釈培養法:所定の希釈系列の微生物含有試料液を調
製し、これを培養管内に接種して培養し、その生育状態
に基づいて統計的に微生物量を定量する方法など。Dilution culture method: A method in which a predetermined dilution series of a microorganism-containing sample solution is prepared, inoculated into a culture tube and cultured, and the amount of microorganisms is statistically quantified based on the growth state.
一方、微生物ではないが、微生物と同様に各種媒体中で
障害を及ぼす物質として発熱性物質(バイロジェン)が
知られており、これらの定量も公衆衛生や品質管理上望
まれており、ことに注射用蒸留水、透析用蒸留水等の蒸
留水中の発熱性物質の定量は公衆衛生上重要である。On the other hand, pyrogenic substances (virogens) are known as substances that are not microorganisms but cause damage in various media like microorganisms, and their quantitative determination is also desired in public health and quality control. Quantification of pyrogens in distilled water such as distilled water for use and distilled water for dialysis is important for public health.
かかる発熱性物質の定量法あるいは試験法として、従来
から、対象とする試料をウサギに注射して生じるウサギ
の体温上昇に基づく方法が広く行なわれている(日本薬
局方;「発熱性物質試験法」参照)が、結果がウサギの
感受性の個体差に左右され易くまた長時間の体温変化の
観測や動物の飼育が伴なうという不都合がある。そこ
で、最近、カブトガニの血球抽出液が発熱性物質と選択
的に反応することを利用し、それによるゲル化度や、発
色性合成基質の存在下の上記反応で生じうるP−ニトロ
アニリンをジアゾ化させた後の吸光度に基づいて発熱性
物質を計測する、いわゆるリムラステストが発熱性物質
の定量、評価法として注目を集めている(肝胆膵12
(4):523−528,1986等)。As a method for quantifying or testing such a pyrogen, a method based on an increase in the body temperature of a rabbit caused by injecting a target sample into a rabbit has been widely performed (Japanese Pharmacopoeia; “Pyrogenic test method”). However, there is a disadvantage that the results are easily influenced by individual differences in rabbit susceptibility and that long-term changes in body temperature are observed and animals are raised. Therefore, recently, by utilizing the fact that the blood cell extract of horseshoe crab selectively reacts with a pyrogen, the gelling degree due to it and the P-nitroaniline which can be generated by the above reaction in the presence of a chromogenic synthetic substrate are diazotized. The so-called limulus test, which measures pyrogenic substances based on the absorbance after conversion, has attracted attention as a method for quantifying and evaluating pyrogenic substances (hepatobiliary pancreas 12
(4): 523-528, 1986).
(ハ)発明が解決しようとする課題 しかしながら、前記従来の微生物の定量方法では、測定
操作に時間がかかると共に、操作が煩雑で熟練を要する
という問題があり、しかも微生物量の定量範囲が狭くか
つ測定の信頼性に欠けるという問題点があった。また、
連続測定に適用できないという問題もあった。(C) Problem to be Solved by the Invention However, in the conventional method for quantifying microorganisms, there is a problem that the measurement operation takes time, the operation is complicated and requires skill, and the quantification range of the amount of microorganisms is narrow and There is a problem that the reliability of measurement is lacking. Also,
There is also a problem that it cannot be applied to continuous measurement.
一方、前記従来の発熱性物質の定量、評価法において
も、操作に時間がかかると共に高価なカブトガニの抽出
液を用いる点でコスト上不利であり、さらに操作が煩雑
で熟練を要し、連続測定に適さないという問題があっ
た。On the other hand, even in the conventional method for quantifying and evaluating an exothermic substance, the operation is time-consuming and costly in terms of using an expensive horseshoe crab extract, and the operation is complicated and requires skill, and continuous measurement is required. There was a problem that it was not suitable for.
この発明は、かかる状況に鑑みなされたものであり、こ
とに短時間で簡便にかつ信頼性良く微生物や発熱性物質
の量を定量でき、さらに連続測定にも適した方法及び装
置を提供しようとするものである。The present invention has been made in view of the above circumstances, and particularly to provide a method and a device that can easily and reliably quantify the amounts of microorganisms and pyrogenic substances in a short time, and that are also suitable for continuous measurement. To do.
(ニ)課題を解決するための手段及び作用 かくしてこの発明は、微生物(又は発熱性物質)含有試
料液の所定量を全炭素分析計に直接導入してTC(全炭
素)値Aを測定する工程と、上記と同一の微生物(又は
発熱性物質)含有試料液を処理して得られる脱微生物
(又は脱発熱性物質)試料液を全炭素分析計に導入して
TC値Bを測定する工程からなり、上記TC値AからTC値B
を減算して得られる値に基づいて、上記試料液中の微生
物(又は発熱性物質)を定量することを特徴とする微生
物等の定量法が提供される。(D) Means and Actions for Solving the Problems Thus, according to the present invention, the TC (total carbon) value A is measured by directly introducing a predetermined amount of a sample liquid containing a microorganism (or a pyrogen) into a total carbon analyzer. Introducing the decarbonization (or depyrogenic substance) sample liquid obtained by treating the process and the same sample liquid containing microorganism (or pyrogenic substance) into the total carbon analyzer
It consists of the process of measuring TC value B, and from TC value A to TC value B
A method for quantifying microorganisms and the like is provided, which is characterized by quantifying the microorganisms (or pyrogens) in the sample solution based on the value obtained by subtracting.
さらに、この発明によれば、微生物(発熱性物質)含有
試料液供給部から延設される試料液供給路Iと、同じく
微生物(又は発熱性物質)含有試料液供給部から延設さ
れ途中に微生物(又は発熱性物質)の除去手段を具備し
てなる試料液供給路IIと、試料液供給路Iと試料液供給
路IIのいずれかに切換可能に接続されてなり試料液を液
計量手段に供給しうる計量流路と、液計量手段からの所
定量の試料液を導入しうるよう接続構成された全炭素分
析形を備えてなる微生物等の定量装置が提供される。Further, according to the present invention, the sample liquid supply path I extending from the sample liquid supply unit containing the microorganism (pyrogenic substance) and the sample liquid supply path I extending from the sample liquid supply unit containing the microorganism (or exothermic substance) A sample liquid supply path II having a means for removing microorganisms (or a pyrogen), and a sample solution supply path I which is switchably connected to any one of the sample solution supply path I and the sample solution supply path II. There is provided an apparatus for quantifying microorganisms and the like, which comprises a measuring flow path which can be supplied to a chamber and a total carbon analysis type which is connected so as to introduce a predetermined amount of sample solution from a solution measuring means.
この発明の最も特徴とする点は、微生物や発熱性物質の
定量に全炭素分析計を用いる点にある。かかる全炭素分
析計としては、含炭素物質を酸化して二酸化炭素を生成
させ、この二酸化炭素量を非分散型赤外分析器、導電率
計、熱伝導度検出器等で検出する方式の全炭素分析型が
使用でき、いわゆるTOC計やTC計として市販されている
ものが種々適用可能である。ここで含炭素物質の酸化方
式としては、UV酸化やペルオキソ硫酸カリウム溶液等の
酸化剤酸化により湿気式酸化法と燃焼酸化法があるが、
燃焼酸化法を適用するのが、酸化が最も強力、確実に行
なわれる点で好ましい。この際、適宜酸化触媒が用いら
れてもよく、この例としては例えば白金黒が挙げられ
る。また、燃焼は680〜950℃に加熱した燃焼管内で高純
度空気や酸素ガスの雰囲気下で行なうのが適している。
一方、二酸化炭素の検出は、信頼性、操作性等の点で非
分散型赤外検出器(NDIR)で行なうのが適している。The most characteristic feature of the present invention is that a total carbon analyzer is used to quantify microorganisms and pyrogens. As such a total carbon analyzer, a carbon-containing substance is oxidized to generate carbon dioxide, and the amount of this carbon dioxide is detected by a non-dispersive infrared analyzer, a conductivity meter, a thermal conductivity detector, etc. A carbon analysis type can be used, and various commercially available so-called TOC meters and TC meters are applicable. Here, as the oxidation method of the carbon-containing substance, there are a humidity oxidation method and a combustion oxidation method by UV oxidation or oxidizing agent such as potassium peroxosulfate solution.
It is preferable to use the combustion oxidation method because the oxidation is strongest and surely performed. At this time, an oxidation catalyst may be appropriately used, and examples of this include platinum black. Further, it is suitable to carry out the combustion in a combustion tube heated to 680 to 950 ° C. in an atmosphere of high-purity air or oxygen gas.
On the other hand, it is suitable to detect carbon dioxide with a non-dispersive infrared detector (NDIR) in terms of reliability and operability.
一方、この発明の他の最も特徴とする点は、微生物(又
は発熱性物質)含有試料液を処理に付して得られる脱微
生物試料液や脱発熱性物質試料液を微生物や発熱性物質
の定量に利用する点にある。On the other hand, the other feature of the present invention is that a de-microbiological sample liquid or a depyrogenic substance sample liquid obtained by subjecting a sample liquid containing a microorganism (or a pyrogen) to a treatment of a microorganism or a pyrogenic substance is used. It is used for quantification.
微生物の除去手段としては膜濾過法、吸着処理法、吸収
処理法など微生物が除去できる手段は全て適用できる。
濾過処理又は吸着処理は、微生物含有試料液を瀘過除去
手段又は吸着除去手段に通過させることにより行なうの
が適している。ここで瀘過除去手段としては、ロ紙、メ
ンブランフィルタ、ガラスフィルタ等が挙げられ、これ
らのポア−サイズは、被検液中に存在しうる微生物の大
きさに依存し、測定を意図する微生物群の最小の微生物
を捕促しうる大きさであればよい。通常、限外瀘過膜程
度のポア−サイズのものが適している。As means for removing microorganisms, all means for removing microorganisms such as membrane filtration method, adsorption treatment method and absorption treatment method can be applied.
The filtration process or the adsorption process is suitably performed by passing the microorganism-containing sample liquid through the filtration removal means or the adsorption removal means. Examples of the filter remover include a paper filter, a membrane filter, a glass filter, and the like.The pore size of these filters depends on the size of the microorganisms that can be present in the test liquid, and the microorganisms that are intended to be measured. It may be of a size that can capture the smallest microorganisms in the group. Usually, a pore size equivalent to an ultrafiltration membrane is suitable.
一方、吸着除去手段としては、荷電膜やイオン交換樹脂
が用いられるが、架橋ポリ−N−アルキル−4−ビニル
ピリジニウムハライド等の不溶性ピリジニウム型樹脂が
有効である。On the other hand, a charged membrane or an ion exchange resin is used as the adsorption / removal means, but an insoluble pyridinium type resin such as a crosslinked poly-N-alkyl-4-vinylpyridinium halide is effective.
一方、発熱性物質の除去手段としては、瀘過処理に用い
られる濾紙、逆浸透膜、限外瀘過膜等を用いた瀘過除去
手段が適しており、これらのうち濾紙を用いた瀘過除去
手段が簡便で好ましい。On the other hand, as a means for removing the exothermic substance, a filter paper used for filtration, a reverse osmosis membrane, an ultrafiltration membrane, or the like is suitable. The removal means is simple and preferable.
微生物含有試料液中には、微生物のみならず、培養液由
来の有機物(グルコースなどの糖類)や夾雑有機物(有
機アミン化合物や溶解性高分子)あるいは溶存CO2、炭
酸塩、炭酸イオン等の無機炭素化合物などがしばしば共
存しているため、これを直接上記全炭素分析計に導入し
て得られた値、TC(全炭素)値A、から微生物量を正確
に定量することは困難である。また、発熱性物質は通常
試料中に微量存在するものであり、かつ試料中には他の
有機成分がしばしば共存しうるため、この試料を直接上
記全炭素分析計に導入して得られた値TC値Aから発熱性
物質量を正確に定量することは困難である。In the sample liquid containing microorganisms, not only microorganisms but also organic substances (sugars such as glucose) derived from the culture liquid, contaminant organic substances (organic amine compounds and soluble polymers) or inorganic substances such as dissolved CO 2 , carbonates, carbonate ions, etc. Since carbon compounds and the like often coexist, it is difficult to accurately quantify the amount of microorganisms from the value obtained by directly introducing this into the total carbon analyzer, the TC (total carbon) value A. In addition, exothermic substances are usually present in the sample in trace amounts, and other organic components can often coexist in the sample.Therefore, the value obtained by directly introducing this sample into the total carbon analyzer described above. It is difficult to accurately quantify the amount of pyrogenic substances from the TC value A.
この発明においては、瀘過処理又は吸着処理等された脱
微生物(又は脱発熱性物質)試料液についてのTC値Bが
さらに測定され、TC値AからTC値Bを減算して得られる
値が算出される。前記した瀘過処理又は吸着処理によ
り、微生物(又は発熱性物質)は実質的に除去される
が、他の共存有機物や無機系炭素化合物は除去されず脱
微生物(又は脱発熱性物質)試料液中に残存する。従っ
てTC値AからTC値Bを減算した値は、実質的に元の試料
液中の微生物量や発熱性物質量に対応するものであり、
この値に基づいて微生物や発熱性物質を正確に定量する
ことができる。In the present invention, the TC value B of the demicrobial (or depyrogenic substance) sample solution that has been filtered or adsorbed is further measured, and the value obtained by subtracting the TC value B from the TC value A is It is calculated. Microorganisms (or pyrogens) are substantially removed by the above-mentioned filtration treatment or adsorption treatment, but other coexisting organic substances and inorganic carbon compounds are not removed, and demicrobialization (or depyrogenation) sample liquid Remains inside. Therefore, the value obtained by subtracting the TC value B from the TC value A substantially corresponds to the amount of microorganisms and the amount of pyrogen in the original sample solution,
Microorganisms and pyrogens can be accurately quantified based on this value.
なお、この発明の実施において、微生物や発熱性物質の
除去手段を有さない試料液供給路I及び微生物や発熱性
物質の除去手段を有する試料液供給路IIを液計量手段に
切換可能に流路構成し、かつ液計量手段から所定量の試
料液を全炭素分析計に導入しうるよう構成した装置を用
いると定量をより簡便に行なうことができ、自動化、連
続化等の観点で好ましい。さらに液計量手段としては、
マイクロシリンジの自動計量手段もあるが、バルブ切換
方式のものを用いるのが、自動化、連続化の点で好まし
い。In the practice of the present invention, the sample liquid supply path I having no means for removing microorganisms and exothermic substances and the sample liquid supply path II having means for removing microorganisms and exothermic substances can be switched to liquid measuring means. It is preferable to use an apparatus having a channel structure and configured so that a predetermined amount of the sample liquid can be introduced into the total carbon analyzer from the liquid measuring means, because the quantification can be performed more easily, and automation, continuity, and the like can be achieved. Furthermore, as a liquid measuring means,
There is also an automatic measuring means for a microsyringe, but it is preferable to use a valve switching type in terms of automation and continuity.
ただし、NDIRを2台用いTC値A,TC値Bをそれぞれ同時に
測定する完全連続測定法を行なってもよい。However, a perfect continuous measurement method may be performed in which two NDIR units are used to simultaneously measure the TC value A and the TC value B, respectively.
(ホ)実施例 第1図に示す1はこの発明の方法を実施する微生物等定
量装置の一実施例を示す構成説明図である。図におい
て、微生物(又は発熱性物質)含有試料液を貯留する試
料槽2aと送液ポンプ2bからなる微生物(又は発熱性物
質)含有試料液供給部2から、分岐状に、試料液供給路
I及び試料液供給路IIが管路接続されている。試料液供
給路IIには限外瀘過器からなる微生物(又は発熱性物
質)の瀘過除去手段3が付設されている。試料液供給路
I及びIIの下流は三方弁4に集合してなり、三方弁4の
切換により、試料液は試料液供給路I及びIIのいずれか
一方を通じて計量流路5へ供給される。計量流路5に
は、高圧六方切換バルブ6が接続されており、その切換
により、試料液は排液槽8及び一定長の管路で構成した
液計量手段7のいずれかに試料液を移送する。液計量手
段7内に導入された試料液は、バルブ6の切換により導
入管9を通じて全炭素分析計内に導入される。(E) Example 1 FIG. 1 is an explanatory diagram showing an example of an apparatus for quantifying microorganisms for carrying out the method of the present invention. In the figure, a sample liquid supply path I is branched from a sample liquid supply unit 2 containing a microorganism (or a heat generating substance), which comprises a sample tank 2a for storing a sample liquid containing a microorganism (or a heat generating substance) and a liquid feed pump 2b. And the sample liquid supply path II are connected by a pipeline. The sample solution supply path II is provided with a filter (3) for removing microorganisms (or heat-generating substances) composed of an ultrafilter. Downstream of the sample liquid supply paths I and II are assembled into a three-way valve 4, and by switching the three-way valve 4, the sample liquid is supplied to the measurement flow path 5 through either one of the sample liquid supply paths I and II. A high-pressure hexagonal switching valve 6 is connected to the measurement flow path 5, and by switching the sample solution, the sample solution is transferred to either a drainage tank 8 or a solution measuring means 7 composed of a conduit of a certain length. To do. The sample liquid introduced into the liquid measuring means 7 is introduced into the total carbon analyzer through the introduction pipe 9 by switching the valve 6.
全炭素分析計11は、白金黒を石英ウールにコーティング
した触媒担体層(内径12mm、長さ90mm)を内蔵した石英
ガラス製の燃焼管12、電気加熱器13、ドレンセパレータ
14、電子クーラー16、非分散型赤外検出器18をこの順に
接続してなり、キャリアーガス供給用の高純度空気ボン
ベ21(不純物のHC分、CO分、CO2分が各々1ppm以下の空
気貯留)を備えてなる。なお、図中、10はキャリアガス
供給路を、15,17は各々ドレンポットを、19は流量計
を、20は演算部を、22は流量制御弁を示す。The total carbon analyzer 11 consists of a quartz glass combustion tube 12, an electric heater 13, and a drain separator, which contains a catalyst carrier layer (inner diameter 12 mm, length 90 mm) in which platinum black is coated on quartz wool.
14, an electronic cooler 16, and a non-dispersion type infrared detector 18 are connected in this order, and a high-purity air cylinder 21 (HC, CO, and CO 2 content of impurities is 1 ppm or less for carrier gas supply). Storage). In the figure, 10 is a carrier gas supply passage, 15 and 17 are drain pots, 19 is a flow meter, 20 is a calculation unit, and 22 is a flow control valve.
上記定量装置1を用いた微生物の定量操作について以下
説明する。The quantification operation of microorganisms using the quantification device 1 will be described below.
まず、三方弁4を供給路I側に設定した状態で、送液ポ
ンプ2bを駆動することにより、微生物含有試料液がその
まま計量流路5へ導入される。ここで高圧六方切換バル
ブ6が実線側から破線側へ切換えられ試料液が液計量手
段内に導入され一定時間後液計量手段7内に満たされ
る。ここでバルブ6は実線側に切換えられる。これによ
り、ボンベ21から供給される空気からなるキャリアーガ
スによって液計量手段内に満たされた試料液は圧送され
て、高温加熱された燃焼管12内に導入され、そこで試料
液中に存在する微生物並びに夾雑有機成分は燃焼酸化さ
れて二酸化炭素に変換される。燃焼酸化で副生する水分
はドレンセパレータ14及び電子クーラ16(2℃に冷却)
で気液分離により除去される。燃焼酸化により生成した
二酸化炭素は、炭酸塩等の熱分解で生じた二酸化炭素や
試料中に溶存していた二酸化炭素と共に非分散型赤外分
析器18に移送され、そこでに酸化炭素の吸光度が検出さ
れ、この検出出力に基づいて演算部20でTC値Aが算出さ
れ、記録表示される。First, with the three-way valve 4 set on the supply path I side, by driving the liquid feeding pump 2b, the microorganism-containing sample liquid is directly introduced into the measuring flow path 5. Here, the high-pressure hexagonal switching valve 6 is switched from the solid line side to the broken line side, the sample liquid is introduced into the liquid measuring means, and the liquid measuring means 7 is filled with the sample liquid after a predetermined time. Here, the valve 6 is switched to the solid line side. As a result, the sample liquid filled in the liquid measuring means by the carrier gas consisting of the air supplied from the cylinder 21 is pressure-fed and introduced into the combustion tube 12 heated at a high temperature, where the microorganisms present in the sample liquid are present. In addition, the contaminant organic components are burnt and oxidized and converted into carbon dioxide. Water produced as a by-product of combustion oxidation is drain separator 14 and electronic cooler 16 (cooled to 2 ° C)
Are removed by gas-liquid separation. Carbon dioxide produced by combustion oxidation is transferred to the non-dispersion infrared analyzer 18 together with carbon dioxide produced by thermal decomposition of carbonates and carbon dioxide dissolved in the sample, where the absorbance of carbon oxide is The TC value A is detected, the TC value A is calculated by the calculation unit 20 based on the detected output, and the TC value A is recorded and displayed.
次いで、三方弁4が供給路II側に切換えられ、微生物含
有試料液が瀘過除去手段3を通過することにより得られ
る脱微生物試料液が、計量流路5へ導入され、以下、前
記と同様にその所定量が燃焼管12内に導入される。ここ
で試料液中には実質的に微生物は存在しないが、夾雑有
機成分は前記瀘過除去手段では除去されないため、かか
る有機成分が燃焼酸化されて二酸化炭素に変換され、他
の二酸化炭素と共に吸光度検出され、これに基づいて演
算部20でTC値Bが算出され記録表示される。Next, the three-way valve 4 is switched to the supply path II side, and the demicrobialized sample solution obtained by passing the microorganism-containing sample solution through the filtration removing means 3 is introduced into the measurement channel 5, and the same as the above. Then, a predetermined amount thereof is introduced into the combustion tube 12. Here, substantially no microorganisms are present in the sample solution, but since the contaminating organic components are not removed by the filtration removal means, the organic components are burnt and oxidized to be converted into carbon dioxide, and the absorbance is absorbed together with other carbon dioxide. The TC value B is detected, and the TC value B is calculated based on the detected value and recorded and displayed.
ここでTC値AからTC値Bを減算した値は微生物量に対応
している。従ってこの値により直接微生物が炭素量とし
て定量でき、また予め炭素量と微生物濃度(重量濃度や
個数濃度等)との検量線を作成しておくことにより、上
記減算値に基づいて微生物量を種々の単位で定量できる
こととなる。Here, the value obtained by subtracting the TC value B from the TC value A corresponds to the amount of microorganisms. Therefore, the microorganisms can be directly quantified as the amount of carbon by this value, and by preparing a calibration curve of the amount of carbon and the concentration of microorganisms (weight concentration, number concentration, etc.) in advance, various amounts of microorganisms can be obtained based on the above subtracted values. Can be quantified in units of.
微生物の定量 上記装置を用いて、下記の条件で微生物(乳酸菌)の定
量を行なった。Quantification of microorganisms Microorganisms (lactic acid bacteria) were quantified using the above apparatus under the following conditions.
キャリアーガス流量 150ml/分 加熱温度 680℃ 〔微生物含有試料液〕 生理食塩水(TC約100ppm相当のグルコース含有)1中
に約5.0mgの乳酸菌を混入して調整。Carrier gas flow rate 150ml / min Heating temperature 680 ℃ [Microorganism-containing sample solution] Prepared by mixing approximately 5.0mg of lactic acid bacteria in physiological saline (containing glucose equivalent to TC approximately 100ppm) 1.
ただし、パイロジェンフリーではない。However, it is not pyrogen free.
セルロース製の0.2μm,φ2.5mmメンブランフィルターか
らなる限外瀘過膜を内蔵したもの(減菌済)。Built-in ultrafiltration membrane consisting of 0.2 μm, φ2.5 mm membrane filter made of cellulose (sterilized).
瀘過圧は約0.1Kg/cm2である。The overpressure is about 0.1 Kg / cm 2 .
TC測定用試料注入は5μで、TC校正は640ppmフタル酸
水素カリウム標準値で行なった。The sample injection for TC measurement was 5 μm, and the TC calibration was performed at 640 ppm potassium hydrogen phthalate standard value.
結果を第2図に示す。TC値Aは603.0ppm TC相当、TC値
Bは107.7ppm TC相当であった。したがって乳酸菌は49
5.3ppm TC相当になる。また、TC値Bは約100ppmのバッ
クグラウンド(生理食塩水)に対し良い一致を示し、乳
酸菌除去率が良好であることを示している。Results are shown in FIG. The TC value A was 603.0 ppm TC equivalent, and the TC value B was 107.7 ppm TC equivalent. Therefore, lactic acid bacteria are 49
It is equivalent to 5.3ppm TC. Further, the TC value B shows a good agreement with the background (physiological saline) of about 100 ppm, indicating that the lactic acid bacterium removal rate is good.
発熱性物質の定量 一方、上記第1図の定量装置を用いて発熱性物質の定量
を行なった。用いた試料液は、発熱性物質としてエンド
トキシンを所定量含有するものであり、発熱性物質標準
品(USPレファレンス・エンドトキシン、EC−5)をエ
ンドトキシンフリーの標準液に所定量溶解して調製し
た。Quantification of Pyrogenic Substance On the other hand, quantification of the exothermic substance was carried out using the quantification device shown in FIG. The sample solution used contained a predetermined amount of endotoxin as a pyrogen, and was prepared by dissolving a standard amount of a pyrogen (USP Reference Endotoxin, EC-5) in a standard solution free of endotoxin.
種々の濃度の発熱性物質含有試料液について、前記微生
物の定量法と同様にしてTC値A及びTC値Bを測定し、エ
ンドトキシン濃度として換算した。なお、定量に要する
時間は各々5分以内であった。TC values A and TC values B were measured in the same manner as in the quantification method for microorganisms for sample liquids containing various concentrations of pyrogenic substances, and converted into endotoxin concentrations. The time required for quantification was within 5 minutes.
この結果を、従来のリムラステストによる値と対比して
第3図に示した。The results are shown in FIG. 3 in comparison with the values obtained by the conventional rim lath test.
このように、発熱性物質についての応答の直線性は優れ
ており、リムラステストと同等の正確度の高い定量が行
なえることが判る。図中、プロット−○−はこの発明の
方法による結果、プロット−△−はリムラステストによ
る結果を示すものである。As described above, the linearity of the response for the exothermic substance is excellent, and it can be understood that the quantification can be performed with high accuracy equivalent to that of the limus test. In the figure, Plot- ○ -shows the result by the method of the present invention, and Plot-Δ- shows the result by the rimlas test.
なお、限外瀘過器におけるメンブランフィルターの代わ
りに、逆浸透膜(三酢酸セルロース膜;外径90mm、長さ
420mm;透過水量0.018m3/hr)又はポリスルホン系の限外
瀘過膜(外径40mm、長さ350mm;公称分画分子量6000、透
過水量0.035m3/hr)を用いても、発熱性物質について、
上記と同様の結果が得られた。In place of the membrane filter in the ultrafilter, reverse osmosis membrane (cellulose triacetate membrane; outer diameter 90 mm, length
420 mm; permeated water 0.018 m 3 / hr) or polysulfone ultrafiltration membrane (outer diameter 40 mm, length 350 mm; nominal molecular weight cutoff 6000, permeated water 0.035 m 3 / hr) about,
The same result as above was obtained.
(ヘ)発明の効果 この発明の微生物等の定量法及び定量装置によれば、微
生物や発熱性物質の量を迅速かつ簡便に定量することが
できる。さらにTC値をベースとして定量が行なわれるた
め信頼性の高い定量を行なうことができ、連続測定にも
簡便に適用することができる。(F) Effects of the Invention According to the method and apparatus for quantifying microorganisms and the like of the present invention, the amounts of microorganisms and pyrogenic substances can be quantified quickly and easily. Furthermore, since the TC value is used as the basis for quantification, highly reliable quantification can be performed and it can be easily applied to continuous measurement.
第1図は、この発明の微生物等の定量法を実施する装置
の一実施例を示す構成説明図、第2図及び第3図は、こ
の発明の実施例で得られる分析チャート及び分析結果を
例示するグラフ図である。 1……微生物等定量装置、 2……微生物(又は発熱性物質)含有試料液供給部、 3……瀘過除去手段、4……三方弁、 5……計量流路、6……高圧六方切換バルブ、 7……液計量手段、8……排液槽、 9……導入管、10……キャリアガス供給部、 11……全炭素分析計、12……燃焼管、 13……電気加熱器、14……ドレンセパレータ、 15,17……ドレンポット、 16……電子クーラー、 18……非分散型赤外検出器、19……流量計、 20……演算部、21……高純度空気ボンベ、 22……流量制御弁。FIG. 1 is a structural explanatory view showing an embodiment of an apparatus for carrying out a method for quantifying microorganisms of the present invention, and FIGS. 2 and 3 show an analysis chart and an analysis result obtained in the embodiment of the present invention. It is a graph figure which illustrates. 1 ... Quantitative device for microorganisms, 2 ... Sample liquid supply unit containing microorganisms (or pyrogens), 3 ... Filter removal means, 4 ... Three-way valve, 5 ... Metering flow path, 6 ... High pressure hexagon Switching valve, 7 ... Liquid metering means, 8 ... Drainage tank, 9 ... Introducing pipe, 10 ... Carrier gas supply section, 11 ... Total carbon analyzer, 12 ... Combustion pipe, 13 ... Electric heating Drain, 14 …… Drain separator, 15,17 …… Drain pot, 16 …… Electronic cooler, 18 …… Non-dispersive infrared detector, 19 …… Flowmeter, 20 …… Calculator, 21 …… High purity Air cylinder, 22 ... Flow control valve.
Claims (2)
定量を全炭素分析計に直接導入してTC(全炭素)値Aを
測定する工程と、上記と同一の微生物(又は発熱性物
質)含有試料液を処理して得られる脱微生物(又は脱発
熱性物質)試料液を全炭素分析計に導入してTC値Bを測
定する工程からなり、上記TC値AからTC値Bを減算して
得られる値に基づいて、上記微生物(又は発熱性物質)
含有試料液中の微生物(又は発熱性物質)を定量するこ
とを特徴とする微生物等の定量法。1. A step of measuring a TC (total carbon) value A by directly introducing a predetermined amount of a sample solution containing a microorganism (or a pyrogen) into a total carbon analyzer, and the same microorganism (or pyrogenicity) as described above. Substance) -containing sample solution is introduced into a total carbon analyzer to obtain a demicrobial (or depyrogenic substance) sample solution, and the TC value B is measured. Based on the value obtained by subtraction, the above microorganism (or pyrogen)
A method for quantifying microorganisms and the like, which comprises quantifying microorganisms (or pyrogens) in a contained sample liquid.
部から延設される試料液供給路Iと、同じく微生物(又
は発熱性物質)含有試料液供給部から延設され途中に微
生物(又は発熱性物質)の除去手段を具備してなる試料
液供給路IIと、試料液供給路Iと試料液供給路IIのいず
れかに切換可能に接続されてなり試料液を液計量手段に
供給しうる計量流路と、液計量手段からの所定量の試料
液を導入しうるよう接続構成された全炭素分析計を備え
てなる微生物等定量装置。2. A sample liquid supply path I extending from a sample liquid supply unit containing a microorganism (or a heat-generating substance), and a sample liquid supply path I extending from the sample liquid supply unit containing a microorganism (or a heat-generating substance) and a microorganism ( Or a sample liquid supply path II provided with a means for removing a heat-generating substance, and a sample solution supply path I and a sample solution supply path II which are switchably connected to supply the sample solution to the liquid measuring means. An apparatus for quantifying microorganisms and the like, which comprises a measuring flow path capable of performing measurement and a total carbon analyzer connected so as to introduce a predetermined amount of sample liquid from a liquid measuring means.
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3834188A JPH0773512B2 (en) | 1987-08-12 | 1988-02-19 | Quantitative method and quantification device for microorganisms |
| US07/273,945 US5116736A (en) | 1988-02-19 | 1988-11-21 | Method for the quantitative determination of micro-organisms or pyrogens |
| EP88119687A EP0328749B1 (en) | 1988-02-19 | 1988-11-25 | A method and an apparatus for the quantitative determination of micro-organisms or pyrogens |
| DE8888119687T DE3879171T2 (en) | 1988-02-19 | 1988-11-25 | METHOD AND DEVICE FOR QUANTITATIVELY DETERMINING MICROORGANISMS OR PYROGENS. |
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP20165387 | 1987-08-12 | ||
| JP62-201653 | 1987-08-12 | ||
| JP3834188A JPH0773512B2 (en) | 1987-08-12 | 1988-02-19 | Quantitative method and quantification device for microorganisms |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH01132400A JPH01132400A (en) | 1989-05-24 |
| JPH0773512B2 true JPH0773512B2 (en) | 1995-08-09 |
Family
ID=26377566
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3834188A Expired - Lifetime JPH0773512B2 (en) | 1987-08-12 | 1988-02-19 | Quantitative method and quantification device for microorganisms |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0773512B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5054591B2 (en) * | 2008-03-27 | 2012-10-24 | 株式会社日清製粉グループ本社 | Method for judging the safety of cooked foods stored at refrigerated temperatures |
| JP5251624B2 (en) * | 2009-03-11 | 2013-07-31 | 東亜ディーケーケー株式会社 | Combustion water quality measuring device |
-
1988
- 1988-02-19 JP JP3834188A patent/JPH0773512B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH01132400A (en) | 1989-05-24 |
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