ESTUARINE NITROGEN-RETENTION INDEPENDENTLY ESTIMATED BY THE DENITRIFICATION RATE AND MASS-BALANCE METHODS - A STUDY OF NORSMINDE FJORD, DENMARK

被引:85
作者
NIELSEN, K
NIELSEN, LP
RASMUSSEN, P
机构
[1] AARHUS UNIV, INST BIOL SCI, DEPT MICROBIAL ECOL, DK-8000 AARHUS, DENMARK
[2] WATER CONSULT, DK-4171 GLUMSO, DENMARK
关键词
ESTUARY; EUTROPHIC; DENITRIFICATION; ISOTOPE PAIRING; LOADING; MASS BALANCE; MODEL; NITROGEN; RETENTION;
D O I
10.3354/meps119275
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Nitrogen retention was studied in a small, shallow estuary (Norsminde Fjord, Denmark) by 2 independent methods: (1) measurement of denitrification rate using the isotope pairing technique; and (2) estimation of mass balances established on the basis of hydrodynamic numerical modelling. Denitrification rates were found to range from 100 to 1600 mu mol N m(-2) d(-1), and varied considerably from February to May. The seasonal and spatial variation in denitrification rate was positively related to the water column NO3- concentration. The average annual denitrification rate was 29 kg N ha(-1) yr(-1), or approximately 6 t N yr(-1) for the entire estuary. This compared well with the annual nitrogen retention of approximately 8 t N yr(-1) calculated from the mass balances. Annual denitrification and nitrogen retention in the estuary accounted for approximately 2% and 3%, respectively, of total nitrogen input from the catchment area. These low values are explicable by the high water exchange rate in the estuary, freshwater retention time being 1.5 to 13 d, with minimum values during the winter. The present study therefore lends no support to the widely held assumption that estuarine denitrification generally amounts to 40 to 50 % of the nitrogen input. The findings indicate that in addition to nitrogen input from the land, consideration must also be given to the water residence when estuarine nitrogen retention is being estimated.
引用
收藏
页码:275 / 283
页数:9
相关论文
共 38 条
[1]  
ABBOTT MB, 1981, TRANSPORT MODELS INL, P222
[2]  
AERTEBJERG G, 1991, 40 MIN ENV NAT ENV R
[3]   DENITRIFICATION, DISSIMILATORY REDUCTION OF NITRATE TO AMMONIUM, AND NITRIFICATION IN A BIOTURBATED ESTUARINE SEDIMENT AS MEASURED WITH N-15 AND MICROSENSOR TECHNIQUES [J].
BINNERUP, SJ ;
JENSEN, K ;
REVSBECH, NP ;
JENSEN, MH ;
SORENSEN, J .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1992, 58 (01) :303-313
[4]  
BORUM J, 1995, IN PRESS EUTROPHICAT
[5]  
Boynton W.R., 1982, ESTUARINE COMP, P69, DOI 10.1016/B978-0-12-404070-0.50011-9
[6]   BENTHIC MICROALGAL PRODUCTION AT STELLWAGEN BANK, MASSACHUSETTS BAY, USA [J].
CAHOON, LB ;
BERETICH, GR ;
THOMAS, CJ ;
MCDONALD, AM .
MARINE ECOLOGY PROGRESS SERIES, 1993, 102 (1-2) :179-185
[7]   DENITRIFICATION IN NITRATE-RICH STREAMS - DIURNAL AND SEASONAL-VARIATION RELATED TO BENTHIC OXYGEN-METABOLISM [J].
CHRISTENSEN, PB ;
NIELSEN, LP ;
SORENSEN, J ;
REVSBECH, NP .
LIMNOLOGY AND OCEANOGRAPHY, 1990, 35 (03) :640-651
[8]   AN EXPLICIT SCHEME FOR ADVECTION DIFFUSION MODELING IN 2 DIMENSIONS [J].
EKEBJAERG, L ;
JUSTESEN, P .
COMPUTER METHODS IN APPLIED MECHANICS AND ENGINEERING, 1991, 88 (03) :287-297
[9]  
Greenberg A.E., 1992, P AWWA WAT QUAL TECH
[10]  
HOVMAND MF, 1993, 91 NAT ENV RES I TEC