Tracking the fate of a high concentration groundwater nitrate plume through a fringing marsh: A combined groundwater tracer and in situ isotope enrichment study

A groundwater plume enriched in 15NO3− was created upgradient of a mesohaline salt marsh. By measuring the changes in concentration and isotopic enrichment of NO3−, N2O, N2, NH4+, and particulate organic nitrogen (PON) during plume transport through the marsh, in situ rates of dissimilatory nitrate reduction to ammonium (DNRA) and denitrification (DNF) were estimated, as well as N storage in the reduced N pools. For groundwater discharge within the top 10 cm of marsh, NO3− removal was 90% complete within the 50 cm of marsh nearest the upland border. The peak NO3− loss rate from the plume ranged from 208 to 645 µM d−1. Rates of DNRA (180 µM d−1) and DNF (387–465 µM d−1) processed 30% and 70% of the NO3− load, respectively. Terminal N2 production was approximately equal to N2 production rates during DNF. Comparison of 15N lost from the 15NO3− pool and 15N gained in each of the reduced products accounted for only 22% of the reduced 15N, thus indicating N export from the system. Despite high rates of DNRA, the NH4+ produced was not a long‐term repository for the groundwater‐derived N but was instead rapidly immobilized into marsh PON and retained on longer timescales. The small inventory of 15N in the N2 and N2 pools relative to DNF rates, coincident with an undersaturation of dissolved argon, indicated that denitrified N was exported to the atmosphere on short timescales. The relative magnitudes of DNF and DNRA in conjunction with the immobilization of NH4+ and evasion of N gases dictated the extent of export versus retention of the groundwater NO3− load.

[1]  I. Anderson,et al.  Quantifying groundwater discharge through fringing wetlands to estuaries: Seasonal variability, methods comparison, and implications for wetland‐estuary exchange , 2001 .

[2]  I. Anderson,et al.  Nitrogen cycling through a fringing marsh-aquifer ecotone , 2001 .

[3]  J. Meyer,et al.  Analysis of nitrogen cycling in a forest stream during autumn using a 15N‐tracer addition , 2000 .

[4]  R. Holmes,et al.  NITROGEN FLOW THROUGH THE FOOD WEB IN THE OLIGOHALINE ZONE OF A NEW ENGLAND ESTUARY , 2000 .

[5]  R. Holmes,et al.  NITROGEN BIOGEOCHEMISTRY IN THE OLIGOHALINE ZONE OF A NEW ENGLAND ESTUARY , 2000 .

[6]  B. Nowicki,et al.  The role of sediment denitrification in reducing groundwater-derived nitrate inputs to Nauset Marsh estuary, Cape Cod, Massachusetts , 1999 .

[7]  B. Nowicki,et al.  The discharge of nitrate‐contaminated groundwater from developed shoreline to marsh‐fringed estuary , 1998 .

[8]  K. Nordstrom,et al.  Estuarine shores: evolution, environments, and human alterations , 1998 .

[9]  R. Wetzel,et al.  Development of a process-based nitrogen mass balance model for a Virginia (USA) Spartina alterniflora salt marsh: implications for net DIN flux , 1997 .

[10]  T. Parkin,et al.  Shallow groundwater denitrification rate measurement by acetylene block , 1997 .

[11]  R. Wiegert,et al.  A Field Study of Photosynthetic Capacity and its Response to Nitrogen Fertilization inSpartina alterniflora , 1997 .

[12]  J. Böhlke,et al.  Combined Use of Groundwater Dating, Chemical, and Isotopic Analyses to Resolve the History and Fate of Nitrate Contamination in Two Agricultural Watersheds, Atlantic Coastal Plain, Maryland , 1995 .

[13]  B. L. Howes,et al.  Long-term 15N-nitrogen retention in the vegetated sediments of a New England salt marsh , 1994 .

[14]  G. E. Bennett,et al.  Membrane Inlet Mass Spectrometer for Rapid High-Precision Determination of N2, O2, and Ar in Environmental Water Samples , 1994 .

[15]  B. Ward,et al.  Nitrogen Uptake, Dissolved Organic Nitrogen Release, and New Production , 1994, Science.

[16]  James G. Cooke,et al.  Nutrient Transformations in a Natural Wetland Receiving Sewage Effluent and the Implications for Waste Treatment , 1994 .

[17]  W. Reay,et al.  Sediment-water column nutrient exchanges in southern Chesapeake Bay nearshore environments , 1993 .

[18]  H. Bokuniewicz Analytical descriptions of subaqueous groundwater seepage , 1992 .

[19]  K. Lajtha,et al.  Couplings of watersheds and coastal waters: Sources and consequences of nutrient enrichment in Waquoit Bay, Massachusetts , 1992 .

[20]  R. Wanninkhof Relationship between wind speed and gas exchange over the ocean , 1992 .

[21]  L. Nielsen Denitrification in sediment determined from nitrogen isotope pairing , 1992 .

[22]  A. Giblin,et al.  Nitrogen inputs to a marine embayment: the importance of groundwater , 1990 .

[23]  J. Harvey,et al.  The influence of tidal marshes on upland groundwater discharge to estuaries , 1990 .

[24]  Göran Bengtsson,et al.  Nitrate Reduction in a Groundwater Microcosm Determined by 15N Gas Chromatography-Mass Spectrometry , 1989, Applied and environmental microbiology.

[25]  P. Brooks,et al.  Diffusion method to prepare soil extracts for automated nitrogen-15 analysis , 1989 .

[26]  J. Chanton,et al.  Gas transport from methane‐saturated, tidal freshwater and wetland sediments , 1989 .

[27]  A. S. Goodman,et al.  Quantitative analysis of saltwater-freshwater relationships in groundwater systems—A historical perspective , 1985 .

[28]  D. B. Nedwell,et al.  The influence of nitrate concentration upon the end-products of nitrate dissimilation by bacteria in anaerobic salt marsh sediment , 1985 .

[29]  D. Hammond,et al.  Gas exchange rates across the sediment-water and air-water interfaces in south San Francisco Bay , 1984 .

[30]  R. Weiss,et al.  Nitrous oxide solubility in water and seawater , 1980 .

[31]  J. Teal,et al.  The nitrogen budget of a salt marsh ecosystem , 1979, Nature.

[32]  W. A. Kaplan,et al.  Denitrification in a salt marsh ecosystem1 , 1979 .

[33]  I. Koike,et al.  Denitrification and Ammonia Formation in Anaerobic Coastal Sediments , 1978, Applied and environmental microbiology.

[34]  L. Solórzano DETERMINATION OF AMMONIA IN NATURAL WATERS BY THE PHENOLHYPOCHLORITE METHOD 1 1 This research was fully supported by U.S. Atomic Energy Commission Contract No. ATS (11‐1) GEN 10, P.A. 20. , 1969 .

[35]  M. B. David,et al.  In Situ Measurements of Denitrification in Constructed Wetlands , 1999 .

[36]  R. Spalding,et al.  Aquifer denitrification as interpreted from in situ microcosm experiments , 1998 .

[37]  G. Kling,et al.  A tracer investigation of nitrogen cycling in a pristine tundra river , 1997 .

[38]  R. Knowles Acetylene Inhibition Technique: Development, Advantages, and Potential Problems , 1990 .

[39]  J. S⊘rensen Nitrate reduction in marine sediment: Pathways and interactions with iron and sulfur cycling , 1987 .

[40]  Marsh Sediment NITRIFICATION, NITRATE REDUCTION, AND NITROGEN , 1986 .

[41]  D. Capone,et al.  A groundwater source of nitrate in nearshore marine sediments , 1985, Nature.

[42]  A. Hattori Chapter 6 – DENITRIFICATION AND DISSIMILATORY NITRATE REDUCTION , 1983 .

[43]  R. Delaune,et al.  Nitrate Reduction in Spartina Alterniflora Marsh Soil 1 , 1982 .

[44]  L. Solórzano Determination of ammonia in natural waters by the phenol hypochlorite method , 1969 .