wAbstract
@Diel and synoptic studies were undertaken in Silver Bow Creek,
a small, highly eutrophic stream receiving municipal sewage from
the city of Butte, Montana, USA. During mid-summer baseflow conditions,
oxidation of ammonium from the Butte wastewater treatment plant
created a 2-km long reach marked by nightly hypoxia and extreme
growth of aquatic plants and algae. Large diel cycles in the concentrations
and isotopic compositions of dissolved oxygen (DO) and dissolved
inorganic carbon (DIC) were inversely related, and are explained
by the daily cycle of photosynthesis and respiration, modified
by the effects of nitrification. Nutrification rates were higher
during the day than at night due to a combination of higher water
temperatures and higher DO concentrations. Changes in nitrification
rate imparted diel cycles in the concentrations and N-isotopic
compositions of NO3- and NH4+, whereas total dissolved inorganic
nitrogen (DIN) concentrations and Β15N-DIN values showed
minimal diel variation. Β15N-NH4
steadily increased with distance downstream over a 5 km reach,
whereas Β15N-NO3 showed a more
complex spatial pattern. Plant assimilation caused downstream
decreases in DIN and soluble reactive phosphorous: however, it
was not possible to determine whether the plants assimilated NO3-, NH4+,
or both. An important new finding of this study is the recognition
that synoptic and diel changes in Β18O-DO in the zone
of active nitrification imparted a corresponding change in Β18O-NO3. Future studies examining the O-isotope composition
of nitrate need to consider whether DO has a constant or shifting
isotopic composition at the source of nitrification. The results
of this study underscore the complex and dynamic interactions
between biologically-active solutes in nutrient-rich streams,
and also emphasize the importance of recognizing these cycles
when collecting samples for scientific or monitoring purposes.
Keywords: Nitrification; Dissolved oxygen; Ammonium; Nitrate;
Stable isotope; Respiration; Photosynthesis; Diel; Diurnalx
1. Introduction
@1.1. Site description
2. Methods
3. Results
@3.1. Field parameters and nutrient concentrations
@3.2. Isotopes of water and dissolved oxygen
@3.3. Concentration and isotopic composition of DIC
@3.4. Isotopes of nitrate, ammonium, and N2
4. Discussion
@4.1. Factors affecting DO and DIC
@4.2. Factors affecting nitrate and ammonium
@4.3. Practical implications
5. Conclusions
Acknowledgments
Appendix A. Supplementary data
References