Streams and rivers are major sources of greenhouse gases (GHGs) to the atmosphere, as carbon and nitrogen are converted and outgassed during transport. Although our understanding of drivers of individual GHG fluxes has improved with numerous site‐specific studies and global‐scale compilations, our ability to parse out interrelated physical and biogeochemical drivers of gas concentrations is limited by a lack of consistently collected, temporally continuous samples of GHGs and their associated drivers. We present a first analysis of such a dataset collected by the National Ecological Observatory Network across 27 streams and rivers across ecoclimatic domains of the United States. Average concentrations of CO2ranged from 36.9 ± 0.88 to 404 ± 33
Nutrient monitoring is important for informing management decisions to mitigate eutrophication in aquatic systems. Many nutrient monitoring programs use filter pore sizes that allow microorganisms to pass into samples and/or wait extended times between sample collection and filtration/preservation, allowing microbial processes to alter nutrient concentrations. Here, 34 sites were sampled to determine how filter pore size and filtration timing affected measured ammonium (NH4+) and orthophosphate (ortho‐P) concentrations. Three filter pore sizes (0.22, 0.45, and 0.70
- PAR ID:
- 10386466
- Publisher / Repository:
- Wiley Blackwell (John Wiley & Sons)
- Date Published:
- Journal Name:
- Limnology and Oceanography: Methods
- Volume:
- 21
- Issue:
- 1
- ISSN:
- 1541-5856
- Page Range / eLocation ID:
- p. 1-12
- Format(s):
- Medium: X
- Sponsoring Org:
- National Science Foundation
More Like this
-
Abstract μ mol L−1, CH4from 0.003 ± 0.0003 to 4.99 ± 0.72μ mol L−1, and N2O from 0.015 to 0.04μ mol L−1and spanned ranges of previous global compilations. Both CO2and CH4were strongly affected by physical drivers including mean air temperature and stream slope, as well as by dissolved oxygen and total nitrogen concentrations. N2O was exclusively correlated with total nitrogen concentrations. Results suggested that potential for gas exchange dominated patterns in gas concentrations at the site level, but contributions of in‐stream aerobic and anaerobic metabolism, and groundwater also likely varied across sites. The highest gas concentrations as well as highest variability occurred in low‐gradient, warmer, and nonperennial systems. These results are a first step in providing unprecedented, continuous estimates of GHG flux constrained by temporally variable physical and biogeochemical drivers of GHG production. -
Abstract Reports of aerobic biogenic methane (CH4) have generated new views about CH4sources in nature. We examine this phenomenon in the free‐flowing Yellowstone river wherein CH4concentrations were tracked as a function of environmental conditions, phototrophic microorganisms (using chlorophyll
a , Chla , as proxy), as well as targeted methylated amines known to be associated with this process. CH4was positively correlated with temperature and Chla , although diurnal measurements showed CH4concentrations were greatest during the night and lowest during maximal solar irradiation. CH4efflux from the river surface was greater in quiescent edge waters (71–94μ mol m−2 d) than from open flowing current (~ 57μ mol m−2 d). Attempts to increase flux by disturbing the benthic environment in the quiescent water directly below (~ 1.0 m deep) or at varying distances (0–5 m) upstream of the flux chamber failed to increase surface flux. Glycine betaine (GB), dimethylamine and methylamine (MMA) were observed throughout the summer‐long study, increasing during a period coinciding with a marked decline in Chla , suggesting a lytic event led to their release; however, this did not correspond to increased CH4concentrations. Spiking river water with GB or MMA yielded significantly greater CH4than nonspiked controls, illustrating the metabolic potential of the river microbiome. In summary, this study provides evidence that: (1) phototrophic microorganisms are involved in CH4synthesis in a river environment; (2) the river microbiome possesses the metabolic potential to convert methylated amines to CH4; and (3) river CH4concentrations are dynamic diurnally as well as during the summer active months. -
Abstract Increasing nitrate (NO3−) loading in rivers due to agricultural fertilization alters benthic nitrogen (N) cycling and shifts coastal wetlands from being a net source to net sink of reactive N. Heterotrophic N2fixation that converts N2to reactive N is often assumed negligible in eutrophic ecosystems and excluded in coastal N budget evaluations. We investigated N2fixation and denitrification in response to increasing NO3−loading (0, 10, and 100
μ M) and sediment organic matter (OMsediment) concentrations in the emerging Wax Lake Delta. Continuous flow‐through incubations with30N2addition was applied to measure N2fixation. The variation of N2fixation rates from 0 to 437μ mol N m−2h−1among different NO3−and OMsedimentconcentrations were comparable to the estimated denitrification rates of 141–377μ mol N m−2h−1. Increasing overlying NO3−concentrations reduced N2fixation rates and facilitated denitrification rates at each OMsedimentconcentration. However, 100μ M of overlying NO3−did not thoroughly inhibit N2fixation rates in sites with intermediate and higher OMsedimentconcentrations (189 and 99μ mol N m−2h−1, respectively). Both N2fixation and denitrification increased with increasing OMsedimentconcentrations, but the relative importance of these processes was impacted mostly by overlying NO3−concentration as increasing NO3−switched the dominance of N2fixation to denitrification in benthic N cycling. This study highlights the importance of heterotrophic N2fixation in coastal deltaic floodplains and emphasizes the necessity of including N2fixation quantification in coastal N budget evaluation, not only in oligotrophic environment but also in eutrophic environment. -
Abstract Stream restoration efforts have aimed at increasing hydraulic residence time (HRT) and transient storage (TS) to enhance nutrient uptake, but there have been few controlled studies quantifying HRT and TS influences on nutrient uptake dynamics. We assessed the effects of HRT and TS on ammonium (NH4+) and phosphate (PO43−) uptake through controlled experiments in an artificial channel draining a pristine tropical stream. We experimentally dammed the channel with artificial weirs, to progressively increase HRT, and performed NH4+and PO43−additions to estimate uptake each time a weir was added. We also ran consecutive additions of NH4+and PO43−with no weirs, to evaluate short‐term changes in uptake metrics. Also, NH4+was injected alone to assess potential nitrification. We observed that NH4+and PO43−uptake rates were much greater in the very first addition, probably due to luxury uptake. The weirs increased mean HRT (from 8.5 to 12 min) and depth (from 6.5 to 8.9 cm) and decreased mean water velocity (0.40–0.28 m s−1). Surprisingly, damming decreased the relative size of transient storage zone (storage zone area/channel area,
A s/A from 0.72 to 0.55), indicating that greater depth increasedA , but notA s. Greater HRT increased uptake rates and velocities of both nutrients (p < 0.05). The NH4+conversion to NO3−was estimated at 18% of NH4+consumption, indicating that joint additions to measure NH4+and NO3−uptake would not be feasible in this system. Our results suggest that increases in HRT can lead to a greater short‐term retention of nutrients, with implications for stream management and restoration initiatives. -
Abstract Ponds play a larger role in the global freshwater methane (CH4) budget than predicted from surface area alone. To improve our understanding of pond CH4dynamics, we measured summer CH4production, concentrations, and emissions to the atmosphere in nine Alaskan wetland ponds along with potential physical, chemical, and biological regulators. Pond CH4production (0.64, 0.086–1.3 mmol m−2d−1; median, interquartile range), as assessed with slurry incubations, was positively related to water‐column temperature and chlorophyll
a (Chla ), negatively influenced by oxygen levels, and varied with microbial community structure. Average water‐column CH4concentrations (0.39, 0.21–0.87μ mol L−1) were lower in deeper ponds and at higher oxygen levels, and as expected, they were correlated with diffusive emissions (0.055, 0.024–0.20 mmol m−2d−1) assessed with flux chambers. Based on a mass balance approach, 39–99% of CH4produced in ponds was oxidized. Pond ebullition (3.7, 0.60–24 mmol m−2d−1) was higher and more variable than diffusive emissions. Additionally, pond ebullition rates were better correlated with production rates from the previous month. We also systematically compared the ratio of ebullition to diffusive CH4emissions in our ponds and other northern lakes, which was negatively related to water depth (n = 71), but positively related to Chla (n = 28). Our study sheds light on the factors that influence pond CH4dynamics and demonstrates that pond ebullition is a significant CH4source worthy of continued study.