Nitrogen fixation in a desert stream ecosystem

被引:87
作者
Grimm, NB
Petrone, KC
机构
[1] Department of Zoology, Box 871501, Arizona State University, Tempe
关键词
acetylene reduction; cyanobacteria; desert; N fixation; nutrient budget; stream;
D O I
10.1023/A:1005798410819
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Few measurements of nitrogen fixation exist for streams. Desert streams are warm, well lighted, and often support abundant cyanobacterial populations; thus N-2 fixation may be significant in these N-poor ecosystems. N-2 fixation was measured in situ by acetylene reduction for two patch types (Anabaena mat and an epilithic assemblage). Patch-specific rates were high compared with published values (maximum 775 mu g N-2 [83 mu mol C2H4] mg chl a(-1) h(-1) or 51 mg N-2 [5.4 mmol C2H4] m(-2) h(-1)). Daytime fixation was higher than nighttime fixation, and temperature, light and inorganic N concentration explained 52% of variance in hourly rates over all dates. Diel input-output budgets were constructed on five dates when cyanobacteria were present in the stream. Diel N-2 fixation rates were measured for comparison with reach-scale diel nitrogen retention, to assess the importance of this vector to N economy of the stream. Fixation accounted for up to 85% of net N flux to the benthos, but its importance varied seasonally. Finally, we applied biomass-specific fixation rates to 1992 and 1993 biomass data to obtain seasonal and annual N-2 fixation estimates. Cyanobacteria were absent or rare during winter and spring, thus most of the annual N-2 fixation occurred during summer and autumn. Annual rates of nitrogen fixation for 1992 and 1993 (8.0 g/m(2) and 12.5 g/m(2)) were very high compared to other streams, and moderately high compared to other ecosystems. Like other phenomena in this disturbance-prone ecosystem, nitrogen fixation is strongly influenced by the number and temporal distribution of flood events.
引用
收藏
页码:33 / 61
页数:29
相关论文
共 66 条
[41]   EFFECTS OF COPPER ON PRODUCTION OF PERIPHYTON, NITROGEN-FIXATION AND PROCESSING OF LEAF LITTER IN A SIERRA-NEVADA, CALIFORNIA, STREAM [J].
LELAND, HV ;
CARTER, JL .
FRESHWATER BIOLOGY, 1985, 15 (02) :155-173
[42]   THE PROBLEM OF PATTERN AND SCALE IN ECOLOGY [J].
LEVIN, SA .
ECOLOGY, 1992, 73 (06) :1943-1967
[43]   MOLYBDENUM AND SULFATE AS CONTROLS ON THE ABUNDANCE OF NITROGEN-FIXING CYANOBACTERIA IN SALINE LAKES IN ALBERTA [J].
MARINO, R ;
HOWARTH, RW ;
SHAMESS, J ;
PREPAS, E .
LIMNOLOGY AND OCEANOGRAPHY, 1990, 35 (02) :245-259
[44]  
Melillo J. M., 1981, Ecological Bulletins, V33, P427
[45]  
MURPHY J, 1962, ANAL CHIM ACTA, V26, P31
[46]   NITROGEN BUDGET OF A SUBARCTIC STREAM ALTERED BY BEAVER (CASTOR-CANADENSIS) [J].
NAIMAN, RJ ;
MELILLO, JM .
OECOLOGIA, 1984, 62 (02) :150-155
[47]   TEMPORAL VARIATION IN ENRICHMENT EFFECTS DURING PERIPHYTON SUCCESSION IN A NITROGEN-LIMITED DESERT STREAM ECOSYSTEM [J].
PETERSON, CG ;
GRIMM, NB .
JOURNAL OF THE NORTH AMERICAN BENTHOLOGICAL SOCIETY, 1992, 11 (01) :20-36
[48]  
Pickett S.T., 2007, Ecological understanding, the nature of theory and the theory of nature, Vsecond
[49]  
REDFIELD AC, 1958, AM SCI, V46, P205
[50]   INDIRECT ALUMINUM TOXICITY TO THE GREEN-ALGA SCENEDESMUS THROUGH INCREASED CUPRIC ION ACTIVITY [J].
RUETER, JG ;
OREILLY, KT ;
PETERSEN, RR .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1987, 21 (05) :435-438