JPS62449B2 - - Google Patents
Info
- Publication number
- JPS62449B2 JPS62449B2 JP261686A JP261686A JPS62449B2 JP S62449 B2 JPS62449 B2 JP S62449B2 JP 261686 A JP261686 A JP 261686A JP 261686 A JP261686 A JP 261686A JP S62449 B2 JPS62449 B2 JP S62449B2
- Authority
- JP
- Japan
- Prior art keywords
- nitrogen
- absorbance
- total amount
- measured
- nitrite
- 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
Links
- 238000002835 absorbance Methods 0.000 claims description 39
- 238000000034 method Methods 0.000 claims description 32
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 30
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 claims description 29
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 claims description 27
- 229910052757 nitrogen Inorganic materials 0.000 claims description 15
- 238000000862 absorption spectrum Methods 0.000 claims description 4
- 239000012086 standard solution Substances 0.000 claims description 3
- 239000013535 sea water Substances 0.000 description 10
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 9
- 238000001228 spectrum Methods 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 238000005259 measurement Methods 0.000 description 6
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000007796 conventional method Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000012544 monitoring process Methods 0.000 description 2
- 230000003287 optical effect Effects 0.000 description 2
- 238000002798 spectrophotometry method Methods 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 229910017464 nitrogen compound Inorganic materials 0.000 description 1
- 150000002830 nitrogen compounds Chemical class 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 238000005375 photometry Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
- G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
- G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
- G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
- G01N21/33—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using ultraviolet light
Landscapes
- Physics & Mathematics (AREA)
- Spectroscopy & Molecular Physics (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Investigating Or Analysing Materials By Optical Means (AREA)
Description
〔発明の技術分野〕
本発明は無機態窒素、更に詳しくは水中におけ
る硝酸態窒素及び亜硝酸態窒素の合計の含有量
(以下合量という)を正しく、かつ自動的に測定
する方法に関するものである。
〔従来技術〕
無機態窒素にはアンモニア態窒素、硝酸態窒素
及び亜硝酸態窒素の3態が存在し、これらを廃水
に混ぜて放流、特に内海や湖へ放流すると、水域
の赤潮発生の原因となる。そこで関係者は無機態
窒素含有廃液を流さないよう努力を続けているが
一方では放流に対する監視体制、特に自動的に水
中の無機態窒素の含有量を測定する方法の確立に
も努力が払われている。
無機態窒素3態のうち、アンモニア態窒素の含
有量についてはイオン選択性電極を使つて一応相
当の精度をもつて測定することができるのでその
自動測定はいまやさして重要な課題ではないが、
硝酸態窒素と亜硝酸態窒素の合量を自動測定する
方法の確立は重要な課題となつている。
ところが、上記窒素を単独で測定する方法は存
在するが、合量を測定する有効な方法はない。
例えばこれまで水中の硝酸態窒素の定量法とし
て、アール・エル・ヤングらのボーラログラフを
用いる方法、エル・アール・マツケンジーらのイ
オン選択性電極による方法、エス・シヤハイネら
による吸光光度法やビー・ケー・アフグハンらに
よるケイ光光度法があり、また、硝酸態窒素の紫
外部吸収測定法として210nmにおける吸光度測
定法、210nmにおける吸光度から275nmにおけ
る吸光度の4倍を差引く方法、220nmにおける
吸光度から275における吸光度の2.5倍を差引く方
法または215nm、220nm、205nm、210nm、
225nm、230nmにおける吸光度を測定し、複雑
な計算をした後、硝酸態窒素の含有量を求める方
法等がある。
また、亜硝酸態窒素のみを測定する方法として
は特殊な有機試薬を使用する吸光光度法による方
法がある。しかしいずれも硝酸態窒素と亜硝酸態
窒素の合量を測定することができない。ただ、英
国特許第1309551号明細書にのみ、水中の有機性
炭素や懸濁物などとともに窒素酸化物の全量を測
定する方法が提案されているが、この方法は複雑
な特殊構造の装置を使用しなければならないので
簡単に、どこでもこの方法を利用して窒素酸化物
を測定することはできない。
硝酸態窒素及び亜硝酸態窒素は共に赤潮発生を
もたらす富栄養化源であるから、それらの個個の
含有量を測定しなくても両者の合量としてそれら
の含有量を容易に、かつ正確に測定することがで
きれば、アンモニア態窒素の測定法と併用して水
中の無機態窒素の測定及び汚染監視体制の強化が
可能となり、工業的または公害防止的な見地から
する極めて意義深い。
一般に吸光光度分析においては、スペクトルの
特定の波長をいくつか選んで、それらの波長にお
ける吸光度を測定し、計算によつて試料中に含ま
れている数種の各成分の各含有量を決定する方法
が公知である。この方法に対し、本発明者の意図
するところは、態様の異なる2種類の窒素化合物
の合量を正しく測定しようとするものであり、そ
の指向する目的に従来と異なる点があると同時
に、むしろ本発明の利用分野を考えれば、発明者
の意図は合理的である。
そこで、本発明者は硝酸態窒素と亜硝酸態窒素
の合量の測定法について鋭意検討した結果、特定
の波長における吸光度を測定してこれに基づく演
算により、上記の含量を正確に測定し得るとの事
実を見い出すに到つた。
〔発明の目的〕
従つて本発明の目的は硝酸態窒素と亜硝酸態窒
素の合量を正確に測定する方法を確立することに
ある。
〔発明の構成〕
すなわち本発明の硝酸態窒素と亜硝酸態窒素の
合量を測定する方法は、硝酸態窒素及び亜硝酸態
窒素がそれぞれ単独に同じ量だけ含まれる二種の
標準試料の紫外線吸収スペクトルS1及びS2の任意
の波長λ2,λ3であつて、前記スペクトルS1と
S2のそれぞれの吸光度E21とE22との差(E21−
E22)及びE31とE32との差(E31−E32)が等しくな
るような波長λ2とλ3における標準溶液の吸光
度E2,E3を測定し、一方、被測定試料について
も同様に前記波長λ2とλ3における吸光度
E′2,E′3を測定し、ランバード・ベルの法則に基
づきE2−E3とE′2−E′3とから被測定試料中の硝酸
態窒素と亜硝酸態窒素の合量を算出することを特
徴とするものである。
具体的に図を用いて本発明法を説明する。まず
硝酸態窒素と亜硝酸態窒素がそれぞれ単独に同じ
量、例えば1.0p.p.mだけ含まれる二種の人工海
水の標準試料をつくり、対照液として窒素を含ま
ない人工海水を用い10.0nmのセル中におけるこ
れらの紫外線吸光度を測定しスペクトルを得る。
すると第1図のごときスペクトルが得られる。即
ち曲線Aが硝酸態窒素の紫外線吸収スペクトルS1
であり、曲線Bが亜硝酸態窒素の紫外線吸収スペ
クトルS2であり、両スペクトルS1とS2とは波長λ
1=219nmのところで交錯し、吸光度E1=0.3を
示す。他方その波長λ1より大きい波長λ4のと
ころでも二つのスペクトルS1とS2とが交錯し、そ
の間におけるスペクトルS1とS2において、任意の
波長λ2,λ3であつて、しかも、その波長λ2
とλ3におけるスペクトルS1とS2のそれぞれの吸
光度E21,E22とE31,E32の差(E21−E22)と(E31
−E32)が等しくなるようなλ2とλ3が存在す
る。上記1.0p.p.mの試料においてはλ2=223n
m、λ3=232nm、E21=0.21、E22=0.07、E31
=0.26、E32=0.12である。本発明においては次
に窒素酸化物の含有量を測定せんとする試料の上
記λ2とλ3における試料の吸光度E2及びE3を
測定し、吸光度の差(E2−E3)を算出し、ランバ
ード・ベルの法則を利用して硝酸態窒素と亜硝酸
態窒素の合量を求めるのである。
かくのごとくすれば硝酸態窒素と亜硝酸態窒素
の個々の含有量を求めてそれらを合量することな
く、ただちに水中の上記二態の窒素の合量を正し
く測定することができる。
すなわち、上記λ2とλ3においては、硝酸態
窒素と亜硝酸態窒素のいずれについても、同じ含
有量の場合は同じ吸光度差(E2−E3)を与える
が、もし別の波長で測定すれば、両態窒素が異な
つた吸光度を示すので、測定値は不正確となる。
〔発明の効果〕
このように、本発明による測定法ではλ2,λ
3のおのおのが、両態窒素について同じ(E2−
E3)を与えるように選定されるがゆえに、測定の
高精度が保証されるのである。
〔実施例〕
次に実施例をもつて本発明の効果を示す。
実施例 1
硝酸態窒素と亜硝酸態窒素の合量が1.0p.p.m
であり、各々の割合が異なる人工海水をつくり、
波長223nmと232nmにおける吸光度E2とE3を測
定し、その差を算出した結果を第2図の曲線に示
した。この曲線は硝酸態窒素と亜硝酸態窒素の割
合が変化しても吸光度に変化がないこと、すなわ
ち本発明法は正確であることを示している。
この実施例において、測定結果の精度を計算し
たところ、変動係数の値で、最小が4.2%、最大
で7.5%であり、本発明法の精度は高いことがわ
かつた。また、硝酸態窒素と亜硝酸態窒素の合量
が2.0p.p.mであり、各々の割合が異なる人工海
水をつくり、同様の測定をした結果、測定された
吸光度E2,E3から算出した吸光度差(E2−E3)は
合量1.0p.p.mの場合の正確に2倍であつた。同
様に計算した精度も変動係数の値で最小2.1%、
最大3.3%であつた。
実施例 2
硝酸態窒素と亜硝酸態窒素の混合割合が1:1
であり、全窒素量、すなわち両態の合量の含有量
を種々変化させた人工海水を作り、λ2=223n
mにおける吸光度E2、λ3=232nmにおける吸
光度E3を測定し、吸光度差(E2−E3)を算出し
た。その結果は第3図に示すとおりである。
これからわかるように人工海水中の全窒素含有
量が高くなれば、直線的に吸光度差(E2−E3)が
高くなり、これによつて、本発明による測定法に
よれば正しく両態窒素の合量が決定できることが
わかる。
実施例 3
硝酸態窒素0.80p.p.m、亜硝酸態窒素0.20p.p.
m、合量1.00p.p.mの人工海水に各種の有機物や
無機物を種々の量共存させて、それらと相互作用
があるか否かを検討した。この場合、λ2=
223nmにおける吸光度E2、λ3=232nmにおけ
る吸光度E3を測定し、吸光度差(E′2−E′3)を算
出した。
一方、共存物質を含まない、上記と同一の硝酸
態及び亜硝酸態濃度の人工海水(標準試料)につ
いても同様に吸光度差(E2−E3)を求め、(E2−
E3)と(E′2−E′3)とからランバード・ベルの法則
によつて硝酸態窒素と亜硝酸態窒素の合量を算出
し、その誤差を求めた。結果を第1表に示す。
[Technical Field of the Invention] The present invention relates to a method for correctly and automatically measuring inorganic nitrogen, more specifically, the total content of nitrate nitrogen and nitrite nitrogen (hereinafter referred to as the total amount) in water. be. [Prior art] Inorganic nitrogen exists in three states: ammonia nitrogen, nitrate nitrogen, and nitrite nitrogen, and when these are mixed with wastewater and released, especially into inland seas and lakes, they can cause red tide in water bodies. becomes. Therefore, those involved are continuing to make efforts to prevent inorganic nitrogen-containing wastewater from being discharged, but efforts are also being made to establish a monitoring system for discharge, especially a method to automatically measure the content of inorganic nitrogen in water. ing. Among the three forms of inorganic nitrogen, the content of ammonia nitrogen can be measured with considerable accuracy using an ion-selective electrode, so automatic measurement is not an important issue at the moment.
Establishing a method to automatically measure the total amount of nitrate nitrogen and nitrite nitrogen is an important issue. However, although there are methods for measuring nitrogen alone, there is no effective method for measuring the total amount. For example, conventional methods for quantifying nitrate nitrogen in water include a method using a bolagraph by R.L. Young et al., a method using an ion-selective electrode by L.R. Matsukenzie et al., a method using an ion-selective electrode by S.・There is a fluorescence photometry method by K. Afghan et al., and methods for measuring the ultraviolet absorption of nitrate nitrogen include a method of measuring absorbance at 210 nm, a method of subtracting four times the absorbance at 275 nm from the absorbance at 210 nm, and a method of subtracting four times the absorbance at 275 nm from the absorbance at 220 nm. Method of subtracting 2.5 times the absorbance at 275 or 215nm, 220nm, 205nm, 210nm,
There are methods such as measuring the absorbance at 225 nm and 230 nm and calculating the nitrate nitrogen content after performing complicated calculations. Further, as a method for measuring only nitrite nitrogen, there is a method using a spectrophotometric method using a special organic reagent. However, neither method can measure the total amount of nitrate nitrogen and nitrite nitrogen. However, only British Patent No. 1309551 proposes a method for measuring the total amount of nitrogen oxides as well as organic carbon and suspended matter in water, but this method uses a device with a complicated special structure. Because it has to be done easily, nitrogen oxides cannot be measured everywhere using this method. Since both nitrate nitrogen and nitrite nitrogen are eutrophication sources that cause red tide, it is easy and accurate to calculate their total content without measuring their individual contents. If this method can be used in combination with the method for measuring ammonia nitrogen, it will be possible to measure inorganic nitrogen in water and strengthen the pollution monitoring system, which is extremely significant from an industrial or pollution prevention standpoint. In general, in spectrophotometric analysis, a number of specific wavelengths in the spectrum are selected, the absorbance at those wavelengths is measured, and the content of each of the several components contained in the sample is determined by calculation. Methods are known. The inventor's intention with this method is to accurately measure the total amount of two types of nitrogen compounds with different embodiments, and at the same time that the intended purpose is different from the conventional method, it is rather Considering the field of application of the present invention, the inventor's intention is reasonable. Therefore, the inventors of the present invention have conducted intensive studies on methods for measuring the total amount of nitrate nitrogen and nitrite nitrogen, and have found that the above content can be accurately measured by measuring the absorbance at a specific wavelength and performing calculations based on this. I have come to discover this fact. [Object of the Invention] Therefore, an object of the present invention is to establish a method for accurately measuring the total amount of nitrate nitrogen and nitrite nitrogen. [Structure of the Invention] That is, the method of measuring the total amount of nitrate nitrogen and nitrite nitrogen of the present invention is to measure the total amount of nitrate nitrogen and nitrite nitrogen using ultraviolet rays of two standard samples each containing the same amount of nitrate nitrogen and nitrite nitrogen. arbitrary wavelengths λ 2 and λ 3 of the absorption spectra S 1 and S 2 ,
The difference between the respective absorbances E 21 and E 22 of S 2 (E 21 −
E 22 ) and the absorbance E 2 and E 3 of the standard solution at wavelengths λ 2 and λ 3 such that the difference (E 31 − E 32 ) between E 31 and E 32 are equal are measured. Similarly, the absorbance at the wavelengths λ 2 and λ 3 is
Measure E′ 2 and E′ 3 , and calculate the total amount of nitrate nitrogen and nitrite nitrogen in the sample to be measured from E 2 −E 3 and E′ 2 −E′ 3 based on the Lambard-Bell law. It is characterized by calculating. The method of the present invention will be specifically explained using figures. First, two standard samples of artificial seawater containing the same amount of nitrate nitrogen and nitrite nitrogen, for example, 1.0 ppm, were prepared, and artificial seawater containing no nitrogen was used as a control solution. Measure the absorbance of these ultraviolet rays to obtain a spectrum.
Then, a spectrum as shown in FIG. 1 is obtained. That is, curve A is the ultraviolet absorption spectrum of nitrate nitrogen S 1
, curve B is the ultraviolet absorption spectrum S 2 of nitrite nitrogen, and both spectra S 1 and S 2 are at the wavelength λ
1 = 219 nm and exhibits absorbance E 1 = 0.3. On the other hand, the two spectra S 1 and S 2 also intersect at the wavelength λ 4 which is larger than the wavelength λ 1, and in the spectra S 1 and S 2 between them, the wavelengths λ 2 and λ 3 are arbitrary, and Its wavelength λ 2
The difference between the absorbances E 21 , E 22 and E 31 , E 32 of spectra S 1 and S 2 at
−E 32 ) are equal to λ 2 and λ 3 . In the above 1.0ppm sample, λ 2 = 223n
m, λ 3 = 232 nm, E 21 = 0.21, E 22 = 0.07, E 31
= 0.26, E 32 = 0.12. In the present invention, next, the absorbances E 2 and E 3 of the sample whose nitrogen oxide content is to be measured are measured at the above λ 2 and λ 3 , and the difference in absorbance (E 2 - E 3 ) is calculated. Then, the total amount of nitrate nitrogen and nitrite nitrogen is determined using Lambard-Bell's law. In this way, the total amount of the above two nitrogen states in water can be immediately and accurately measured without determining the individual contents of nitrate nitrogen and nitrite nitrogen and adding them together. In other words, in the above λ 2 and λ 3 , the same absorbance difference (E 2 - E 3 ) will be given for both nitrate nitrogen and nitrite nitrogen if the content is the same, but if they are measured at different wavelengths, In this case, the measurement value will be inaccurate because the two nitrogen states will have different absorbances. [Effect of the invention] As described above, in the measurement method according to the present invention, λ 2 , λ
3 are the same for amphoteric nitrogen (E 2 −
E 3 ), a high accuracy of measurement is guaranteed. [Example] Next, the effects of the present invention will be shown with examples. Example 1 Total amount of nitrate nitrogen and nitrite nitrogen is 1.0 ppm
, and create artificial seawater with different proportions of each.
The absorbances E 2 and E 3 at wavelengths of 223 nm and 232 nm were measured, and the difference between them was calculated, and the results are shown in the curve of FIG. 2. This curve shows that the absorbance does not change even if the ratio of nitrate nitrogen to nitrite nitrogen changes, that is, the method of the present invention is accurate. In this example, when the accuracy of the measurement results was calculated, the minimum coefficient of variation was 4.2% and the maximum was 7.5%, indicating that the accuracy of the method of the present invention was high. In addition, we created artificial seawater in which the total amount of nitrate nitrogen and nitrite nitrogen was 2.0 ppm, and the proportions of each were different. As a result of similar measurements, the absorbance difference calculated from the measured absorbances E 2 and E 3 was (E 2 −E 3 ) was exactly twice that in the case of a total amount of 1.0 ppm. The accuracy calculated in the same way is a minimum of 2.1% for the coefficient of variation.
The maximum was 3.3%. Example 2 Mixing ratio of nitrate nitrogen and nitrite nitrogen is 1:1
, we created artificial seawater with various amounts of total nitrogen, that is, the total content of both nitrogen states, and found that λ 2 = 223n
The absorbance E 2 at m and the absorbance E 3 at λ 3 =232 nm were measured, and the absorbance difference (E 2 −E 3 ) was calculated. The results are shown in Figure 3. As can be seen from this, as the total nitrogen content in artificial seawater increases, the absorbance difference (E 2 − E 3 ) increases linearly. It can be seen that the total amount of can be determined. Example 3 Nitrate nitrogen 0.80ppm, nitrite nitrogen 0.20ppm
We coexisted various amounts of various organic and inorganic substances in artificial seawater with a total concentration of 1.00 ppm, and examined whether they interacted with each other. In this case, λ 2 =
The absorbance E 2 at 223 nm and the absorbance E 3 at λ 3 =232 nm were measured, and the absorbance difference (E′ 2 −E′ 3 ) was calculated. On the other hand, the absorbance difference (E 2 − E 3 ) was determined in the same way for artificial seawater (standard sample) with the same nitrate and nitrite concentrations as above, which does not contain coexisting substances, and (E 2 −
The total amount of nitrate nitrogen and nitrite nitrogen was calculated from E 3 ) and (E′ 2 −E′ 3 ) according to Lambard-Bell's law, and the error was determined. The results are shown in Table 1.
【表】
第1表からわかるように、E2−E3の値は、比
較的大量の有機物や無機物の共存下で少ない誤差
で測定することができ、したがつて硝酸態窒素と
亜硝酸態窒素の合量を正しく決定することができ
る。
実施例 4
神戸港湾内の海水中の硝酸態窒素と亜硝酸態窒
素の合量をλ2=223nmにおける吸光度E2,λ
3=232nmにおける吸光度E3を測定し、吸光度
差(E2−E3)を算出することによつて求めた。そ
の場合10.0mmと50.0mmの2種のセルをつかい、2
回ずつ測定を行なつた。一方、標準溶液について
も同様に前記二波長における吸光度を測定して吸
光度差を算出し、ランバード・ベルの法則を利用
して第2表の結果を得た。[Table] As can be seen from Table 1, the value of E 2 −E 3 can be measured with a small error in the coexistence of relatively large amounts of organic and inorganic substances, and therefore The total amount of nitrogen can be determined correctly. Example 4 The total amount of nitrate nitrogen and nitrite nitrogen in the seawater in Kobe Port is expressed as the absorbance E 2 and λ at λ 2 = 223 nm.
It was determined by measuring the absorbance E3 at 3 =232 nm and calculating the absorbance difference ( E2 - E3 ). In that case, use two types of cells, 10.0 mm and 50.0 mm, and
Measurements were taken one time at a time. On the other hand, for the standard solution, the absorbance at the two wavelengths was similarly measured, the absorbance difference was calculated, and the results shown in Table 2 were obtained using the Lambard-Bell law.
【表】
第2表からわかるように、光路長10.0mmのセル
を用いた場合も、また50.0mmのセルを用いた場合
も同じ測定値が得られた。また測定した海水中の
硝酸態窒素と亜硝酸態窒素の合量は、約0.3〜
0.4p.p.mであることもわかつた。[Table] As can be seen from Table 2, the same measured values were obtained when using a cell with an optical path length of 10.0 mm and when using a cell with an optical path length of 50.0 mm. In addition, the total amount of nitrate nitrogen and nitrite nitrogen in the seawater measured was approximately 0.3~
It was also found that it was 0.4ppm.
第1図は本発明の原理を説明するための図面で
あり、また、第2及び3図は本発明の一実施例の
結果を示す図面である。
FIG. 1 is a diagram for explaining the principle of the present invention, and FIGS. 2 and 3 are diagrams showing the results of an embodiment of the present invention.
Claims (1)
に同じ量だけ含まれる二種の標準試料の紫外線吸
収スペクトルS1及びS2の任意の波長λ2,λ3で
あつて、前記スペクトルS1とS2のそれぞれの吸光
度E21とE22との差(E21−E22)及びE31とE32との
差(E31−E32)が等しくなるような波長λ2とλ
3における標準溶液の吸光度E2,E3を測定し、
一方、被測定試料についても同様に前記波長λ2
とλ3における吸光度E′2,E′3を測定し、ランバ
ード・ベルの法則に基づきE2−E3とE′2−E′3とか
ら被測定試料中の硝酸態窒素と亜硝酸態窒素の合
量を算出することを特徴とする硝酸態窒素と亜硝
酸態窒素の合量を測定する方法。1 Arbitrary wavelengths λ 2 and λ 3 of the ultraviolet absorption spectra S 1 and S 2 of two standard samples containing the same amounts of nitrate nitrogen and nitrite nitrogen, respectively; Wavelengths λ 2 and λ such that the difference between absorbances E 21 and E 22 (E 21 - E 22 ) and the difference between E 31 and E 32 (E 31 - E 32 ) of S 2 are equal.
Measure the absorbance E 2 and E 3 of the standard solution in 3 ,
On the other hand, similarly for the sample to be measured, the wavelength λ 2
The absorbances E ′ 2 and E ′ 3 at A method for measuring the total amount of nitrate nitrogen and nitrite nitrogen, characterized by calculating the total amount of nitrogen.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP261686A JPS61172031A (en) | 1986-01-09 | 1986-01-09 | Method for measuring combined amount of nitrate nitrogen and nitrite nitrogen |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP261686A JPS61172031A (en) | 1986-01-09 | 1986-01-09 | Method for measuring combined amount of nitrate nitrogen and nitrite nitrogen |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10516376A Division JPS5330379A (en) | 1976-09-01 | 1976-09-01 | Measurement of inorganic form nitrogen |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61172031A JPS61172031A (en) | 1986-08-02 |
| JPS62449B2 true JPS62449B2 (en) | 1987-01-08 |
Family
ID=11534334
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP261686A Granted JPS61172031A (en) | 1986-01-09 | 1986-01-09 | Method for measuring combined amount of nitrate nitrogen and nitrite nitrogen |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61172031A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63130342U (en) * | 1987-02-20 | 1988-08-25 | ||
| JPH01293281A (en) * | 1988-05-20 | 1989-11-27 | Inoue Mtp Co Ltd | Spoiler |
| JPH0314745A (en) * | 1989-06-12 | 1991-01-23 | Koito Mfg Co Ltd | Lighting fixture for car |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0619326B2 (en) * | 1987-02-05 | 1994-03-16 | 環境エンジニアリング株式会社 | Method for quantifying inorganic nitrogen |
| JPH0196533A (en) * | 1987-10-07 | 1989-04-14 | Agency Of Ind Science & Technol | Method for measuring total nitrogen by eliminating influence of bromide |
| JP3355901B2 (en) * | 1995-12-27 | 2002-12-09 | 信越半導体株式会社 | Compound semiconductor epitaxial wafer |
| DE10228929A1 (en) * | 2002-06-28 | 2004-01-15 | Endress + Hauser Conducta Gesellschaft für Mess- und Regeltechnik mbH + Co. KG | Arrangement for measuring the nitrate content in liquids |
| CN104155258A (en) * | 2014-08-15 | 2014-11-19 | 广州衡创测试技术服务有限公司 | Improved determination method for total nitrogen in water |
| JP7032729B2 (en) * | 2017-12-15 | 2022-03-09 | 国立大学法人豊橋技術科学大学 | Nitrate ion and nitrite ion concentration detection method and concentration detection device and plant growth / life-prolonging agent manufacturing device |
-
1986
- 1986-01-09 JP JP261686A patent/JPS61172031A/en active Granted
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63130342U (en) * | 1987-02-20 | 1988-08-25 | ||
| JPH01293281A (en) * | 1988-05-20 | 1989-11-27 | Inoue Mtp Co Ltd | Spoiler |
| JPH0314745A (en) * | 1989-06-12 | 1991-01-23 | Koito Mfg Co Ltd | Lighting fixture for car |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61172031A (en) | 1986-08-02 |
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