Grantee Research Project Results
Nitrogen Removal in Constructed Wetlands: Enhancement of Nitrate Mass Transfer in the Denitrification Zone
EPA Grant Number: U915482Title: Nitrogen Removal in Constructed Wetlands: Enhancement of Nitrate Mass Transfer in the Denitrification Zone
Investigators: Fleming-Singer, Maia S.
Institution: University of California - Berkeley
EPA Project Officer: Packard, Benjamin H
Project Period: January 1, 1998 through January 1, 2001
Project Amount: $26,408
RFA: STAR Graduate Fellowships (1998) RFA Text | Recipients Lists
Research Category: Fellowship - Environmental , Safer Chemicals , Academic Fellowships
Objective:
The objective of this research project is to explore three hypotheses regarding control and enhancement of denitrification rates in constructed wetlands designed for nitrogen removal. The central hypothesis is the following: (1) denitrification in constructed wetlands follows first-order kinetics with respect to nitrate; (2) denitrification rates can be enhanced by increasing mass transfer of nitrate from the bulk water to the denitrification zone; and (3) promotion of a denitrifying episediment zone will enhance denitrification rates above those found in purely sediment-based denitrification zones.
Approach:
Laboratory bench-scale wetland microcosms and field-scale mesocosms will be used to measure denitrification rates and nitrate mass transfer under four experimental conditions. Two of the experimental conditions will focus on a sediment-based denitrification zone. In these experiments, a clearly defined sediment-water interface will be promoted to test the extent of nitrate mass transfer from the overlying water into the sediments for denitrification. The efficacy of an episediment denitrification zone will be tested under the two remaining experimental conditions, using a constructed thatch of cattail leaves and stems positioned at the sediment-water interface. The laboratory microcosms will be flow-through, temperature- controlled (20 EC), anoxic (N2 sparged), and will include sediments, water column, and a headspace. Nitrate levels in the microcosm influent will be manipulated within the 1-100 mg/L range, based on realistic-constructed wetland concentrations. Steady-state effluent nitrate concentrations will be measured using ion chromatography, and denitrification rates will be calculated by nitrate mass balance. To determine the location and extent of the denitrification zone, water column and sediment vertical profiles of nitrate and chloride (a conservative species) also will be measured at steady state using a thin-film polyacrylamide gel sampler. Multiway Analysis of Variance (ANOVA) will be used to evaluate statistical differences between treatments, while linear regression and/or curve fitting will be used to determine the appropriate relationship between denitrification rate and nitrate concentration within treatments. Assessment of surface area and microbial populations will be conducted in all treatments.
I expect to find that episediment denitrification is greater than denitrification in a purely sediment-based wetland. First-order kinetics should be apparent in the sediment-based treatments because of a diffusional mass transfer limitation of nitrate. However, denitrification in episediments may follow zero-order or mixed-order kinetics because of the lack of a diffusional constraint.
Supplemental Keywords:
fellowship, microcosms, nitrogen removal, wetlands, denitrification, mesocosms, ion chromatography, nitrate mass balance, nitrate, chloride, episediment, nitrate, effluent, polyacrylamide, influent., RFA, Scientific Discipline, Water, Ecosystem Protection/Environmental Exposure & Risk, Aquatic Ecosystems & Estuarine Research, Water & Watershed, exploratory research environmental biology, Environmental Chemistry, Ecosystem/Assessment/Indicators, Ecosystem Protection, Chemistry, Restoration, Aquatic Ecosystem, Microbiology, Ecological Effects - Environmental Exposure & Risk, Environmental Microbiology, Biochemistry, Aquatic Ecosystem Restoration, Biology, Engineering, Chemistry, & Physics, Watersheds, Ecological Indicators, wetlands, microbial degradation, mass spectrometry, nitrates, wetland ecosystem, Ammonia, spectroscopic studies, microbial communities, nitrogen cycling, spectroscopy, nitrification/denitrification, microbial breakdown, nitrate removal, nitrogen compounds, carbon availability, wetland responses, nitorgen cycling, microbial floraProgress and Final Reports:
The perspectives, information and conclusions conveyed in research project abstracts, progress reports, final reports, journal abstracts and journal publications convey the viewpoints of the principal investigator and may not represent the views and policies of ORD and EPA. Conclusions drawn by the principal investigators have not been reviewed by the Agency.