Affiliation:
1. Departments of Crop and Soil Sciences and of Microbiology and Public Health, Michigan State University, East Lansing, Michigan 48824
Abstract
A more sensitive analytical method for NO
3
−
was developed based on the conversion of NO
3
−
to N
2
O by a denitrifier that could not reduce N
2
O further. The improved detectability resulted from the high sensitivity of the
63
Ni electron capture gas chromatographic detector for N
2
O and the purification of the nitrogen afforded by the transformation of the N to a gaseous product with a low atmospheric background. The selected denitrifier quantitatively converted NO
3
−
to N
2
O within 10 min. The optimum measurement range was from 0.5 to 50 ppb (50 μg/liter) of NO
3
−
N, and the detection limit was 0.2 ppb of N. The values measured by the denitrifier method compared well with those measured by the high-pressure liquid chromatographic UV method above 2 ppb of N, which is the detection limit of the latter method. It should be possible to analyze all types of samples for nitrate, except those with inhibiting substances, by this method. To illustrate the use of the denitrifier method, NO
3
−
concentrations of <2 ppb of NO
3
−
N were measured in distilled and deionized purified water samples and in anaerobic lake water samples, but were not detected at the surface of the sediment. The denitrifier method was also used to measure the atom% of
15
N in NO
3
−
. This method avoids the incomplete reduction and contamination of the NO
3
−
-N by the NH
4
+
and N
2
pools which can occur by the conventional method of
15
NO
3
−
analysis. N
2
O-producing denitrifier strains were also used to measure the apparent
K
m
values for NO
3
−
use by these organisms. Analysis of N
2
O production by use of a progress curve yielded
K
m
values of 1.7 and 1.8 μM NO
3
−
for the two denitrifier strains studied.
Publisher
American Society for Microbiology
Subject
Ecology,Applied Microbiology and Biotechnology,Food Science,Biotechnology
Reference18 articles.
1. Isotope labeling studies on the mechanism of N-N bond formation in denitrification;Aerssens E.;J. Biol. Chem.,1986
2. Bard Y. 1974. Nonlinear parameter estimation. Academic Press Inc. New York.
3. Kinetic explanation for accumulation of nitrite, nitric oxide, and nitrous oxide during bacterial denitrification;Betlach M. R.;Appl. Environ. Microbiol.,1981
4. Seasonal variation in numbers and activity of denitrifying bacteria in soil. Taxonomy and physiological groups among isolates;Christensen S.;Tidsskrift Planteavi,1985
5. Oxygen sensitivity prevents denitrifiers and barley plant roots from directly competing for nitrate;Christensen S.;FEMS Microbiol. Ecol.,1988
Cited by
74 articles.
订阅此论文施引文献
订阅此论文施引文献,注册后可以免费订阅5篇论文的施引文献,订阅后可以查看论文全部施引文献