Comparison of isotope pairing and N2:Ar methods for measuring sediment-denitrification-assumptions, modifications, and implications

被引:188
作者
Eyre, BD
Rysgaard, S
Dalsgaard, T
Christensen, PB
机构
[1] So Cross Univ, Ctr Coastal Management, Lismore 2480, Australia
[2] Natl Environm Res Inst, DK-8600 Silkeborg, Denmark
来源
ESTUARIES | 2002年 / 25卷 / 6A期
关键词
D O I
10.1007/BF02692205
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Denitrification has been measured during the last few years using two different methods in particular: isotope pairing measured on a triple-collector isotopic ratio mass spectrometer and N-2:Ar ratios measured on a membrane inlet mass spectrometer (MIMS). This study compares these two techniques in short-term batch experiments. Rates obtained using the original N-2:Ar method were up to 3 to 4 times higher than rates obtained using the isotope pairing technique due to O-2 reacting with the N-2 during MIMS analysis. Oxygen combines with N-2 within the mass spectrometer ion source forming NO+ which reduces the N-2 concentration. The decrease in N-2 is least at lower O-2 concentrations and since oxygen is typically consumed during incubations of sediment cores, the result is often a pseudo-increase in N-2 concentration being interpreted as denitrification activity. The magnitude of, this oxygen effect may be instrument, specific. The reaction of O-2 with N-2 and the subsequent decrease in N-2 was only partly corrected using an O-2 correction curve for the relationship between N-2 and O-2 concentrations. The O-2 corrected N-2:Ar denitrification rates were-lower, but still did not match the isotope pairing rates and the variability between replicates was much higher. Using a copper reduction column heated to 600degreesC to remove all of the O-2 from the sample before MIMS analysis resulted in comparable rates (slightly-lower), and comparable variability between replicates, to the isotope pairing technique. The N-2:Ar technique determines the net N-2 production as the difference between N-2 production by denitrification and N-2 Consumption by N-fixation, while N-fixation has little effect on the isotope pairing technique which determines a rate very close to the gross N-2 production. When. the two different techniques were applied on the same sediment, the small difference in rates obtained by the two methods seemed to reflect N-fixation as also supported from measurements of ethylene production in acetylene enriched sediment cores. The N-2:Ar and isotope pairing techniques may be combined to provide simultaneous measurements of denitrification and N-fixation. Both techniques have several assumptions that must be met to achieve accurate rates; a number of tests are outlined that can be applied to demonstrate that these assumptions are being meet.
引用
收藏
页码:1077 / 1087
页数:11
相关论文
共 39 条
[1]   An improved chromatographic method to measure nitrogen, oxygen, argon and methane in gas or liquid samples [J].
An, SM ;
Joye, SB .
MARINE CHEMISTRY, 1997, 59 (1-2) :63-70
[2]   Simultaneous measurement of denitrification and nitrogen fixation using isotope pairing with membrane inlet mass spectrometry analysis [J].
An, SM ;
Gardner, WS ;
Kana, T .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 2001, 67 (03) :1171-1178
[3]  
[Anonymous], EUTROPHICATION COAST
[4]   Benthic nutrient recycling in Port Phillip Bay, Australia [J].
Berelson, WM ;
Heggie, D ;
Longmore, A ;
Kilgore, T ;
Nicholson, G ;
Skyring, G .
ESTUARINE COASTAL AND SHELF SCIENCE, 1998, 46 (06) :917-934
[5]   NANOGRAM NITRITE AND NITRATE DETERMINATION IN ENVIRONMENTAL AND BIOLOGICAL-MATERIALS BY VANADIUM(III) REDUCTION WITH CHEMI-LUMINESCENCE DETECTION [J].
BRAMAN, RS ;
HENDRIX, SA .
ANALYTICAL CHEMISTRY, 1989, 61 (24) :2715-2718
[6]  
BROAST CW, 1988, SOIL SCI SOC AM J, V52, P1317
[7]  
Capone DG., 1993, HDB METHODS AQUATIC, P621, DOI 10.1201/9780203752746-74
[8]  
CHRISTENSEN PB, COMMMUNICATION
[9]  
CORNWELL J, COMMUNICATION
[10]   Denitrification in coastal ecosystems: methods, environmental controls, and ecosystem level controls, a review [J].
Jeffrey C. Cornwell ;
W. Michael Kemp ;
Todd M. Kana .
Aquatic Ecology, 1999, 33 (1) :41-54