title: Measuring ammonia concentrations and emissions from agricultural land and liquid surfaces: a review.
abstract: Aerial ammonia concentrations (Cg) are measured using acid scrubbers, filter packs, denuders, or optical methods. Using Cg and wind speed or airflow rate, ammonia emission rate or flux can be directly estimated using enclosures or micrometeorological methods. Using nitrogen (N) recovery is not recommended, mainly because the different gaseous N components cannot be separated. Although low cost and replicable, chambers modify environmental conditions and are suitable only for comparing treatments. Wind tunnels do not modify environmental conditions as much as chambers, but they may not be appropriate for determining ammonia fluxes; however, they can be used to compare emissions and test models. Larger wind tunnels that also simulate natural wind profiles may be more useful for comparing treatments than micrometeorological methods because the latter require larger plots and are, thus, difficult to replicate. For determining absolute ammonia flux, the micrometeorological methods are the most suitable because they are nonintrusive. For use with micrometeorological methods, both the passive denuders and optical methods give comparable accuracies, although the latter give real-time Cg but at a higher cost. The passive denuder is wind weighted and also costs less than forced-air Cg measurement methods, but it requires calibration. When ammonia contamination during sample preparation and handling is a concern and separating the gas-phase ammonia and aerosol ammonium is not required, the scrubber is preferred over the passive denuder. The photothermal interferometer, because of its low detection limit and robustness, may hold potential for use in agriculture, but it requires evaluation. With its simpler theoretical basis and fewer restrictions, the integrated horizontal flux (IHF) method is preferable over other micrometeorological methods, particularly for lagoons, where berms and land-lagoon boundaries modify wind flow and flux gradients. With uniform wind flow, the ZINST method requiring measurement at one predetermined height may perform comparably to the IHF method but at a lower cost.
authors.affiliation: Biological and Agricultural Engineering Department, North Carolina State University, Raleigh, NC 27695-7625, USA. sanjay_shah@ncsu.edu
authors.forename: Sanjay B
authors.initials: SB
authors.lastname: Shah
authors.forename: Philip W
authors.initials: PW
authors.lastname: Westerman
authors.forename: Jactone
authors.initials: J
authors.lastname: Arogo
mesh_terms: D000383:Agriculture; D000393:Air Pollutants / Q000032:analysis*; D000641:Ammonia / Q000032:analysis*; D004784:Environmental Monitoring / Q000379:methods*; D008372:Manure; D012037:Refuse Disposal; D014835:Volatilization; D014865:Waste Disposal, Fluid
chemical_list: D000393:Air Pollutants; D008372:Manure; D000641:Ammonia