Abstract:Increased application of nitrogen (N) fertilizers in agricultural systems contributes to significant environmental impacts, including eutrophication of fresh and coastal waters. Rice cutgrass [ (L.) Sw.] can significantly enhance denitrification potential in agricultural ditch sediments and potentially reduce N export from agricultural watersheds, but relationships with known drivers are not well understood. To address this, we examined effects of nitrate (NO) availability on dinitrogen gas (N) and NO fluxes s… Show more
“…The V max values measured in P. australis vegetated sediments during summer (∼10,000 mg N m −2 d −1 ) were 10-60 times greater than the values measured for a variety of emergent plants incubated under similar water temperature conditions (Table 2). Wintertime V max values measured in the present experiment also were markedly greater than those reported by Messer, Burchell, Birgand, Broome, & Chescheir (2017) and Speir et al (2017) for Schoenoplectus tabernaemontani (C.C. Gmel.)…”
Section: Discussioncontrasting
confidence: 74%
“…Wintertime V max values measured in the present experiment also were markedly greater than those reported by Messer, Burchell, Birgand, Broome, & Chescheir () and Speir et al. () for Schoenoplectus tabernaemontani (C.C. Gmel.)…”
Section: Discussioncontrasting
confidence: 70%
“…Conversely, P. australis demonstrated a weaker affinity for NO 3 − compared with other macrophytes such as Carex appressa R. Br. (Payne et al., ) and Leersia oryzoides (Speir et al., ). By affecting denitrification drivers (i.e.…”
Section: Discussionmentioning
confidence: 99%
“…Recently, we parameterized factors that regulate denitrification rates associated with P. australis , including the role of water velocity and biofilm presence (Castaldelli et al., ; Soana, Gavioli, et al., ). In addition, others have started to investigate the role of NO 3 − availability on plant‐mediated denitrification for a variety of species (Messer, Burchell, Birgand, Broome, & Chescheir, 2017; Speir, Taylor, & Scott, ), but to our knowledge, there is no literature describing relationships between denitrification rates and NO 3 − availability in sediments vegetated with P. australis .…”
Understanding relationships between an increase in nitrate (NO3−) loading and the corresponding effects of wetland vegetation on denitrification is essential to designing, restoring, and managing wetlands and canals to maximize their effectiveness as buffers against eutrophication. Although Phragmites australis (Cav.) Trin. ex Steud. is frequently used to remediate nitrogen (N) pollution, no information is available on how NO3− concentration may affect plant‐mediated denitrification. In the present study, denitrification was measured in outdoor vegetated and unvegetated mesocosms incubated in both summer and winter. After spiking the mesocosms with NO3− concentrations typical of agricultural drainage water (0.7−11.2 mg N L−1), denitrification was quantified by the simultaneous measurement of NO3− consumption and dinitrogen gas (N2) production. Although denitrification rates varied with vegetation presence and season, NO3− availability exerted a significant positive effect on the process. Vegetated sediments were more efficient than bare sediments in adapting their mitigation potential to an increase in NO3−, by yielding a one‐order‐of‐magnitude increase in NO3− removal rates, under both summer (743−6007 mg N m−2 d−1) and winter (43−302 mg N m−2 d−1) conditions along the NO3− gradient. Denitrification was the dominant sink for water NO3− in winter and only for vegetated sediments in summer. Nitrification likely contributed to fuel denitrification in summer unvegetated sediments. Since denitrification rates followed Michaelis–Menten kinetics, P. australis‐mediated depuration may be considered optimal up to 5.0 mg N L−1. The present outcomes provide experimentally supported evidence that restoration with P. australis can work as a cost‐effective means of improving water quality in agricultural watersheds.
“…The V max values measured in P. australis vegetated sediments during summer (∼10,000 mg N m −2 d −1 ) were 10-60 times greater than the values measured for a variety of emergent plants incubated under similar water temperature conditions (Table 2). Wintertime V max values measured in the present experiment also were markedly greater than those reported by Messer, Burchell, Birgand, Broome, & Chescheir (2017) and Speir et al (2017) for Schoenoplectus tabernaemontani (C.C. Gmel.)…”
Section: Discussioncontrasting
confidence: 74%
“…Wintertime V max values measured in the present experiment also were markedly greater than those reported by Messer, Burchell, Birgand, Broome, & Chescheir () and Speir et al. () for Schoenoplectus tabernaemontani (C.C. Gmel.)…”
Section: Discussioncontrasting
confidence: 70%
“…Conversely, P. australis demonstrated a weaker affinity for NO 3 − compared with other macrophytes such as Carex appressa R. Br. (Payne et al., ) and Leersia oryzoides (Speir et al., ). By affecting denitrification drivers (i.e.…”
Section: Discussionmentioning
confidence: 99%
“…Recently, we parameterized factors that regulate denitrification rates associated with P. australis , including the role of water velocity and biofilm presence (Castaldelli et al., ; Soana, Gavioli, et al., ). In addition, others have started to investigate the role of NO 3 − availability on plant‐mediated denitrification for a variety of species (Messer, Burchell, Birgand, Broome, & Chescheir, 2017; Speir, Taylor, & Scott, ), but to our knowledge, there is no literature describing relationships between denitrification rates and NO 3 − availability in sediments vegetated with P. australis .…”
Understanding relationships between an increase in nitrate (NO3−) loading and the corresponding effects of wetland vegetation on denitrification is essential to designing, restoring, and managing wetlands and canals to maximize their effectiveness as buffers against eutrophication. Although Phragmites australis (Cav.) Trin. ex Steud. is frequently used to remediate nitrogen (N) pollution, no information is available on how NO3− concentration may affect plant‐mediated denitrification. In the present study, denitrification was measured in outdoor vegetated and unvegetated mesocosms incubated in both summer and winter. After spiking the mesocosms with NO3− concentrations typical of agricultural drainage water (0.7−11.2 mg N L−1), denitrification was quantified by the simultaneous measurement of NO3− consumption and dinitrogen gas (N2) production. Although denitrification rates varied with vegetation presence and season, NO3− availability exerted a significant positive effect on the process. Vegetated sediments were more efficient than bare sediments in adapting their mitigation potential to an increase in NO3−, by yielding a one‐order‐of‐magnitude increase in NO3− removal rates, under both summer (743−6007 mg N m−2 d−1) and winter (43−302 mg N m−2 d−1) conditions along the NO3− gradient. Denitrification was the dominant sink for water NO3− in winter and only for vegetated sediments in summer. Nitrification likely contributed to fuel denitrification in summer unvegetated sediments. Since denitrification rates followed Michaelis–Menten kinetics, P. australis‐mediated depuration may be considered optimal up to 5.0 mg N L−1. The present outcomes provide experimentally supported evidence that restoration with P. australis can work as a cost‐effective means of improving water quality in agricultural watersheds.
“…Hanrahan et al () used sacrificial microcosm incubations and membrane‐inlet mass spectrometry (MIMS) to compare rates from different habitat zones within two‐stage ditches. Alternatively, continuous flow‐through incubations of intact sediment cores rely on core removal from ditch habitats and incubations in flow‐through laboratory settings to measure gas fluxes (Taylor et al ; Speir et al ). All of these methods rely on incubations in the dark at a constant temperature.…”
There is keen interest to enhance denitrification within intervening aquatic habitats between agricultural areas and downstream aquatic ecosystems to reduce nitrogen (N) loading impacts to receiving ecosystems. We conducted a series of measurements to examine whole system in situ diel denitrification estimates in experimental ditch and stream environments using a Bayesian one-station diel N 2 flux model. Model estimates revealed complex patterns that indicate fluxes may be controlled by the balance of both N 2 production via denitrification and consumption driven by physical or biological processes associated with strong diel patterns in environmental conditions. We investigated potential improvements in model fits to observed data associated with the addition of a N 2 consumption term to represent biological (N 2 fixation) or physical (bubble formation and N 2 scavenging) mechanisms associated with daytime photosynthesis. We also expanded the current one-station diel flux model to a two-station model to estimate denitrification in discrete reaches. Our modified diel N 2 flux models improved model fit significantly across three metrics (Nash-Sutcliffe efficiency, root mean square ratio, and percent bias) increasing their utility in shallow, open canopy, lotic systems. While more studies are needed to understand specific mechanisms associated with N 2 consumption processes in small agricultural drainages as well as environmental conditions affecting their relative importance, these results improve estimates of N 2 flux where dynamic conditions and heterogeneity of habitats create severe diel patterns in factors controlling dissolved gas concentrations and prohibit accurate estimates of N 2 flux using existing models.
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