2007
DOI: 10.1051/limn/2007026
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Comparative use of field and laboratory mesocosms for in-stream nitrate uptake measurement

Abstract: Recent publications suggest that in large watersheds a large proportion (20 to 70%) of the net nitrogen input to the aquatic environment may be removed during water's downstream path towards the outlet. In small watersheds there are few to no evaluations of the importance of in-stream processes in the overall nitrogen budget due in part to the lack of simple and robust methods for measuring in-stream nitrate uptake. We propose a comparative study for laboratory and field measurements on open mesocosms, 30 cm i… Show more

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Cited by 13 publications
(5 citation statements)
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“…The zero order, first order, and Monod models were chosen because they have been used to model NO 3 -N removal in wetlands in past experiments [25,36]. The efficiency loss model was chosen because to our knowledge it had not been explored prior to this study in wetlands, but has been observed to model NO 3 -N removal well in streams [37][38][39].…”
Section: No 3 -N Removal Kinetic Modelsmentioning
confidence: 99%
See 1 more Smart Citation
“…The zero order, first order, and Monod models were chosen because they have been used to model NO 3 -N removal in wetlands in past experiments [25,36]. The efficiency loss model was chosen because to our knowledge it had not been explored prior to this study in wetlands, but has been observed to model NO 3 -N removal well in streams [37][38][39].…”
Section: No 3 -N Removal Kinetic Modelsmentioning
confidence: 99%
“…The ρ FO , the mass transfer coefficient (cm d −1 ), accounts for the intrinsic ability for the soil to retain NO 3 -N by including depth, which is often ignored by using other removal rate constants (i.e., k (d −1 )) in first order decay model evaluations. The model can be expressed mathematically as [37]:…”
Section: First Order Decay (Fo) Modelmentioning
confidence: 99%
“…Few applications considered the potential reversal of flow at the interface and its impact on nitrate removal at the catchment scale (Conan et al, 2003;Galbiati et al, 2006), but until today the exact quantification of the intensity of the removal due to various processes occurring at the stream-aquifer interface remains uncertain (Flipo et al, 2007a). Although certain control factors of biogeochemical processes occurring at the stream-aquifer interface are known, such as water residence time, nitrate concentration or organic matter content (Carleton and Montas, 2010;Dahm et al, 1998;Hill et al, 1998;Kjellin et al, 2007;Peyrard et al, 2011;Rivett et al, 2008;Weng et al, 2003), as well as water level fluctuations (Burt et al, 2002;Dahm et al, 1998;Hefting et al, 2004;Turlan et al, 2007), numerical models remain limited by their ability to simulate water pathways in the interface properly (Burt, 2005). Consequently, largescale biogeochemical models lack predictive abilities with regard to climate change issues or the assessment of the implementation of environmental regulatory frameworks, such as the European Water Framework Directive (WFD) (Parliament Council of the European Union, 2000).…”
Section: Introductionmentioning
confidence: 99%
“…Paul and Meyer, 2001). Nutrient uptakes rates are interesting indicators of the biogeochemical function of streams and the ability to quantify this uptake function (Turlan et al, 2007). Stream metabolism and stream communities affect the processes that influence nutrient uptake rates and thus nutrients loads, but it is not yet clear from the literature what are the respective contributions of these processes to nutrient uptake rate variations (Newbold et al, 1981).…”
Section: Introductionmentioning
confidence: 99%