Determination of N-species in soil extracts using microplate techniques
Colourimetric methods for the determination of NO 3 −, NH 4 + and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO 2 − using a solution of hydrazine sulphate. Ammonium in the soil extracts was puri...
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Published in | Talanta (Oxford) Vol. 74; no. 4; pp. 648 - 654 |
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Main Authors | , , |
Format | Journal Article |
Language | English |
Published |
Amsterdam
Elsevier B.V
15.01.2008
Oxford Elsevier |
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Abstract | Colourimetric methods for the determination of NO
3
−, NH
4
+ and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO
2
− using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH
3 from small volumes (750
μL) of extract treated with MgO into a H
2SO
4 collector using a double-plate, MicroResp™ method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K
2S
2O
8 at 110
°C in a 96
×
1.1
mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO
3
−. The recovery of N, measured as NO
3
−, from NH
4NO
3 and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020
mg
N
L
−1 for NO
3
− and 0.051
mg
N
L
−1 for NH
4
+. The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO
3
− was 1.03× result from ion chromatography
+
0.0055 (
R
2
=
0.9961); for NH
4
+ determined by the microplate method, the relationship was 0.9696
×
result from a discrete analyser
−
0.0169 (
R
2
=
0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435
×
result obtained by combustion
+
0.0489 (
R
2
=
0.9743). Purification of the NH
4
+ in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired
t-test,
p
=
0.05) between measured concentration values determined before and after diffusion. |
---|---|
AbstractList | Colourimetric methods for the determination of NO
3
−, NH
4
+ and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO
2
− using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH
3 from small volumes (750
μL) of extract treated with MgO into a H
2SO
4 collector using a double-plate, MicroResp™ method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K
2S
2O
8 at 110
°C in a 96
×
1.1
mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO
3
−. The recovery of N, measured as NO
3
−, from NH
4NO
3 and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020
mg
N
L
−1 for NO
3
− and 0.051
mg
N
L
−1 for NH
4
+. The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO
3
− was 1.03× result from ion chromatography
+
0.0055 (
R
2
=
0.9961); for NH
4
+ determined by the microplate method, the relationship was 0.9696
×
result from a discrete analyser
−
0.0169 (
R
2
=
0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435
×
result obtained by combustion
+
0.0489 (
R
2
=
0.9743). Purification of the NH
4
+ in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired
t-test,
p
=
0.05) between measured concentration values determined before and after diffusion. Colourimetric methods for the determination of NO(3)(-), NH(4)(+) and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO(2)(-) using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH(3) from small volumes (750microL) of extract treated with MgO into a H(2)SO(4) collector using a double-plate, MicroResp method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K(2)S(2)O(8) at 110 degrees C in a 96x1.1mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO(3)(-). The recovery of N, measured as NO(3)(-), from NH(4)NO(3) and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020mgNL(-1) for NO(3)(-) and 0.051mgNL(-1) for NH(4)(+). The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO(3)(-) was 1.03x result from ion chromatography+0.0055 (R(2)=0.9961); for NH(4)(+) determined by the microplate method, the relationship was 0.9696xresult from a discrete analyser-0.0169 (R(2)=0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435xresult obtained by combustion+0.0489 (R(2)=0.9743). Purification of the NH(4)(+) in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired t-test, p=0.05) between measured concentration values determined before and after diffusion.Colourimetric methods for the determination of NO(3)(-), NH(4)(+) and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO(2)(-) using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH(3) from small volumes (750microL) of extract treated with MgO into a H(2)SO(4) collector using a double-plate, MicroResp method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K(2)S(2)O(8) at 110 degrees C in a 96x1.1mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO(3)(-). The recovery of N, measured as NO(3)(-), from NH(4)NO(3) and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020mgNL(-1) for NO(3)(-) and 0.051mgNL(-1) for NH(4)(+). The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO(3)(-) was 1.03x result from ion chromatography+0.0055 (R(2)=0.9961); for NH(4)(+) determined by the microplate method, the relationship was 0.9696xresult from a discrete analyser-0.0169 (R(2)=0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435xresult obtained by combustion+0.0489 (R(2)=0.9743). Purification of the NH(4)(+) in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired t-test, p=0.05) between measured concentration values determined before and after diffusion. Colourimetric methods for the determination of NO(3)(-), NH(4)(+) and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO(2)(-) using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH(3) from small volumes (750microL) of extract treated with MgO into a H(2)SO(4) collector using a double-plate, MicroResp method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K(2)S(2)O(8) at 110 degrees C in a 96x1.1mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO(3)(-). The recovery of N, measured as NO(3)(-), from NH(4)NO(3) and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020mgNL(-1) for NO(3)(-) and 0.051mgNL(-1) for NH(4)(+). The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO(3)(-) was 1.03x result from ion chromatography+0.0055 (R(2)=0.9961); for NH(4)(+) determined by the microplate method, the relationship was 0.9696xresult from a discrete analyser-0.0169 (R(2)=0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435xresult obtained by combustion+0.0489 (R(2)=0.9743). Purification of the NH(4)(+) in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired t-test, p=0.05) between measured concentration values determined before and after diffusion. Colourimetric methods for the determination of NO sub(3) super(-), NH sub(4) super(+) and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate was determined by azo dye formation after reduction to NO sub(2) super(-) using a solution of hydrazine sulphate. Ammonium in the soil extracts was purified and concentrated by diffusion as NH sub(3) from small volumes (750 mu L) of extract treated with MgO into a H sub(2)SO sub(4) collector using a double-plate, MicroResp[TM] method and subsequently determined by the Berthelot reaction. For the determination of total N, samples were oxidised with K sub(2)S sub(2)O sub(8) at 110 degree C in a 96 x 1.1 mL polytetrafluoroethylene block with a lid that closed individual wells. The oxidised solutions were transferred to standard plates for colourimetric analysis of NO sub(3) super(-). The recovery of N, measured as NO sub(3) super(-), from NH sub(4)NO sub(3) and a range of organic-N compounds was >95%. The limits of quantitation of the colourimetic assays were 0.020 mg N L super(-1) for NO sub(3) super(-) and 0.051 mg N L super(-1) for NH sub(4) super(+). The methods were tested on water extracts derived from a range of 10 nutrient poor soils from Scotland. There were acceptable linear correlations between the results obtained by established methods. For soil extracts analysed by the microplate method, the relationship for NO sub(3) super(-) was 1.03x result from ion chromatography + 0.0055 (R super(2) = 0.9961); for NH sub(4) super(+) determined by the microplate method, the relationship was 0.9696 x result from a discrete analyser - 0.0169 (R super(2) = 0.9757) and for total N determined by oxidation in the PTFE microplate the relationship was 0.9435 x result obtained by combustion + 0.0489 (R super(2) = 0.9743). Purification of the NH sub(4) super(+) in water extracts from the 10 different soils by the diffusion method did not result in any systematic difference (paired t-test, p = 0.05) between measured concentration values determined before and after diffusion. |
Author | Shand, Charles A. Coutts, Grace Williams, Berwyn L. |
Author_xml | – sequence: 1 givenname: Charles A. surname: Shand fullname: Shand, Charles A. email: c.shand@macaulay.ac.uk – sequence: 2 givenname: Berwyn L. surname: Williams fullname: Williams, Berwyn L. – sequence: 3 givenname: Grace surname: Coutts fullname: Coutts, Grace |
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Keywords | Colourimetric analysis Ammonium Organic nitrogen Nitrate Diffusion of ammonia Water Chemical analysis Tetrafluoroethylene polymer Combustion Nitrates Sulfuric acid Sample preparation Azo dye Test method Oxidation Diffusion Hydrazine Quantitative analysis Organic compounds Purification Nitrogen Ammonia Soils Ion chromatography Nutrient Nitrogen dioxide |
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Snippet | Colourimetric methods for the determination of NO
3
−, NH
4
+ and total N in water extracts of soils using 96-well microplate techniques are described. Nitrate... Colourimetric methods for the determination of NO(3)(-), NH(4)(+) and total N in water extracts of soils using 96-well microplate techniques are described.... Colourimetric methods for the determination of NO sub(3) super(-), NH sub(4) super(+) and total N in water extracts of soils using 96-well microplate... |
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StartPage | 648 |
SubjectTerms | Ammonium Analytical chemistry Chemistry Chromatographic methods and physical methods associated with chromatography Colourimetric analysis Diffusion of ammonia Exact sciences and technology Indexing in process Nitrate Organic nitrogen Other chromatographic methods Q1 |
Title | Determination of N-species in soil extracts using microplate techniques |
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