HR: 08:15h
AN: A51G-02 [Abstracts]
TI: Mixing Heights and Three-Dimensional Ozone Structure Observed by Airborne Lidar During the 2006 Texas Air Quality Study
AU: * Hardesty, R M
EM: mike.hardesty@noaa.gov
AF: NOAA Earth System Research Laboratory, 325 Broadway, Boulder, CO 80305, United States
AU: Senff, C J
EM: christoph.senff@noaa.gov
AF: Cooperative Institute for Research in Environmental Sciences, University of Colorado at
Boulder, Boulder, CO 80309-0216, United States
AU: Alvarez, R J
EM: raul.alvarez@noaa.gov
AF: NOAA Earth System Research Laboratory, 325 Broadway, Boulder, CO 80305, United States
AU: Banta, R M
EM: robert.banta@noaa.gov
AF: NOAA Earth System Research Laboratory, 325 Broadway, Boulder, CO 80305, United States
AU: Sandberg, S P
EM: scott.sandberg@noaa.gov
AF: NOAA Earth System Research Laboratory, 325 Broadway, Boulder, CO 80305, United States
AU: Weickmann, A M
EM: ann.weickmann@noaa.gov
AF: Cooperative Institute for Research in Environmental Sciences, University of Colorado at
Boulder, Boulder, CO 80309-0216, United States
AU: Darby, L S
EM: lisa.darby@noaa.gov
AF: NOAA Earth System Research Laboratory, 325 Broadway, Boulder, CO 80305, United States
AB:
A new all solid state ozone lidar was deployed on a NOAA Twin Otter to study boundary layer ozone and aerosol,
mostly around Houston, during the 2006 Texas Air Quality Study. The new instrument transmits high pulse-rate,
low pulse-energy light at 3 wavelengths in the ultraviolet to obtain ozone profiles with 500 m horizontal resolution
and 90 m vertical resolution. During the Texas field study, 20 research flights resulted in nearly 70 hours of ozone
measurements during the period from August 1 to September 15. Science objectives included characterization
of background ozone levels over rural areas near Houston and Dallas and variability and structure of the boundary
layer over different surface types, including urban, wooded, and agricultural land surface areas as well as over
Galveston Bay and the Gulf of Mexico. A histogram of all boundary layer ozone concentration measurements
showed a bimodal distribution with modes at 45 ppb and 70 ppb. The lower mode correlated with southerly flow,
when relatively clean air was transported onshore into the Houston area. Segmenting the observations during
southerly flow by region, including the Gulf of Mexico, land within about 55 km from the coast, and further inland
indicated that background levels increased by about 10 ppb as air was transported onshore. During the latter
part of the experiment, as more pollution was imported into the Houston region, background levels rose to nearly
80 ppb in regions N of Houston. Two flights aimed at observing import of ozone into Texas from the east showed
that ozone concentrations increased and boundary layer depths deepened upwind of Houston between
September 4 and September 8. Background levels rose by more than 10 ppb over this period.
In addition to ozone measurements, we also estimated boundary layer height based on maximum gradient in
observed backscatter. The technique worked well when the layer topped by the strongest gradient extends down
to the surface. Investigation of the correlation between ozone levels and mixing layer heights both within and
external to the Houston urban plume showed a variety of relationships, depending on, e.g., wind direction and
occurrence of a bay/gulf breeze. On a day-to-day basis, higher ozone levels were weakly correlated with deeper
mixing levels – this was likely due to advection of the urban heat island downwind with the high-ozone urban
plume.
DE: 0345 Pollution: urban and regional (0305, 0478, 4251)
SC: Atmospheric Sciences [A]
MN: 2007 Fall Meeting