Deducing Ground-to-Air Emissions from Observed Trace Gas Concentrations: A Field Trial with Wind Disturbance

Inverse-dispersion techniques allow inference of a gas emission rate Q from measured air concentration. In “ideal surface layer problems,” where Monin–Obukhov similarity theory (MOST) describes the winds transporting the gas, the application of the technique can be straightforward. This study examines the accuracy of an ideal MOST-based inference, but in a nonideal setting. From a6m 6 m synthetic area source surrounded by a 20 m 20 m square border of a windbreak fence (1.25 m tall), Q is estimated. Open-path lasers gave line-averaged concentration CL at positions downwind of the source, and an idealized backward Lagrangian stochastic (bLS) dispersion model was used to infer QbLS. Despite the disturbance of the mean wind and turbulence caused by the fence, the QbLS estimates were accurate when ambient winds (measured upwind of the plot) were assumed in the bLS model. In the worst cases, with CL measured adjacent to a plot fence, QbLS overestimated Q by an average of 50%. However, if these near-fence locations are eliminated, QbLS averaged within 2% of the true Q over 61 fifteen-minute observations (with a standard deviation Q/Q 0.20). Poorer accuracy occurred when in-plot wind measurements were used in the bLS model. The results show that when an inverse-dispersion technique is applied to disturbed flows without accounting for the disturbance, the outcome may still be of acceptable accuracy if judgment is applied in the placement of the concentration detector.

[1]  T. W. Horst,et al.  A SIMPLE FORMULA FOR ATTENUATION OF EDDY FLUXES MEASURED WITH FIRST-ORDER-RESPONSE SCALAR SENSORS , 1997 .

[2]  Thomas K. Flesch,et al.  Wind Measurements in a Square Plot Enclosed by a Shelter Fence , 2003 .

[3]  T. Flesch,et al.  Micro-meteorological methods for estimating surface exchange with a disturbed windflow , 2001 .

[4]  Eugene Yee,et al.  Calculation of winds disturbed by an array of fences , 2003 .

[5]  J. Garratt The Atmospheric Boundary Layer , 1992 .

[6]  J. C. Kaimal,et al.  Atmospheric boundary layer flows , 1994 .

[7]  K. Mcnaughton Micrometeorology of shelter belts and forest edges , 1989 .

[8]  Lowry A. Harper,et al.  Deducing Ground-to-Air Emissions from Observed Trace Gas Concentrations: A Field Trial with Wind Disturbance , 2004 .

[9]  John D. Wilson Oblique, Stratified Winds about a Shelter Fence. Part I: Measurements , 2004 .

[10]  D. Shonnard,et al.  An inversion algorithm for determining area-source emissions from downwind concentration measurements. , 1994, Air & waste : journal of the Air & Waste Management Association.

[11]  E. Kanemasu,et al.  Estimating Ammonia Flux: A Comparison Between the Integrated Horizontal Flux Method and Theoretical Solutions of the Diffusion Profile1 , 1985 .

[12]  Hiroshi Sakamoto,et al.  Flow around a cubic body immersed in a turbulent boundary layer , 1982 .

[13]  Atmospheric-stability effect on windbreak shelter and drag , 1975 .

[14]  W. Massman A simple method for estimating frequency response corrections for eddy covariance systems , 2000 .

[15]  Takayuki Tokairin,et al.  Numerical investigation of the effect of road structures on ambient air quality—for their better design , 2004 .

[16]  G. W. Thurtell,et al.  Estimation of the rate of gaseous mass transfer from a surface source plot to the atmosphere , 1982 .