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How well can we model air pollution meteorology in the
Houston area?
Wayne Angevine
CIRES / NOAA ESRL
Mark Zagar
Met. Office of Slovenia
Jerome Brioude, Robert Banta, Christoph Senff, HyunCheol Kim, Daewon Byun
Orientation
Surface sites to be used for temperature and wind comparisons
LaPorte wind profiler in green
Galveston Bay
Gulf of Mexico55km
50km
Orientation
Satellite image on 1 September 2006 1137 LST
Coasts low and sandy, little elevation change or terrain
Measurements and simulations
Texas Air Quality Study II (August-October 2006)
Surface meteorological and pollution monitoring sites
Mixing heights and winds from a radar wind profiler at LaPorte (on land)
WRF simulations
How can we tell if one model run is better than another?
Need metrics that clearly show improved performance
Several approaches:– Traditional bulk statistics– Case studies– Sea breeze and stagnation frequency– Plume locations
WRF simulations
75 days, 1 August – 14 October 2006 5 km inner grid spacing Three styles:
– FDDA of 3 wind profilers, reduced soil moisture, and hourly SST
– FDDA of 3 wind profilers and reduced soil moisture
– Reduced soil moisture only All with ECMWF initialization every 24 hours
(at 0000 UTC) Retrospective runs, not forecasts
Impact of FDDA on wind profile
Full run, all hours FDDA reduces random error in
direction Note this is not an independent
comparison (this data was assimilated)
Red is FDDA run Blue has FDDA, 1-h SST, and
reduced soil moisture Green has reduced soil moisture
only
Impact of FDDA on surface winds
Full run, all hours FDDA reduces random error in
direction (more clearly seen if only daytime hours are considered)
ECMWF has less speed bias at C35 and C45 and less random error in speed at all sites
ECMWF has similar direction bias and random error to WRF runs over all hours, but WRF w/FDDA is better in daytime
Red is FDDA run Blue has FDDA, 1-h SST, and
reduced soil moisture Green has reduced soil moisture
only Black is ECMWF
Impact of FDDA and soil moisture on surface winds
Episode days (17) only Site C45, southeast of Houston very near
Galveston Bay FDDA improves random error in both
speed and direction 1-h SST improves random error in the
afternoon, but makes it worse at night ECMWF has different but comparable
errors, but WRF w/FDDA is better at hours 18 and 21 (and worse at hour 3)
Red is FDDA run Blue has FDDA, 1-h SST, and reduced
soil moisture Green has reduced soil moisture only Black is ECMWF
Impact of FDDA and soil moisture on surface temperatures
When are the errors worst? 10 days have at least one
hour with temperature difference > 5K at site C35 (28 hours total) in FDDA run
All differences > 5K have model > measurement (model too warm)
All 10 days have convection or a cold front in reality
Model also has clouds and fronts but different amount, timing, or location
New metrics:Sea breeze frequency
How often does a sea breeze occur in the simulation AND measurement?
Definition: Northerly component >1 m/s between 0600 and 1200 UTC and southerly >1 m/s after 1200 UTC
FDDA or FDDA+1hSST run closer to measurement at all 7 sites (at least a little)
Results not sensitive to threshold
Red is FDDA runBlue has FDDA, 1-h SST, and reduced soil
moistureGreen has reduced soil moisture only
New metrics:Net trajectory distance
Trajectories starting midway along the Ship Channel at 1400 UTC each day, extending for 10 hours at 190 m AGL
WRF run w/FDDA Comparing total distance to
net distance A rough measure of
recirculation The lower left portion of the
diagram is of most interest
New metrics:Net trajectory distance
Net distance was found by Banta et al. to correlate well with maximum ozone
Also holds for trajectories from WRF simulated winds, shown here
r = -0.85, r2 = 0.72 Run with FDDA Run with 1-h SST about the
same Total distance correlation
much worse (r = -0.57)
New metrics:Vector average wind
Averaging u and v vs. averaging speed
Over 10 hours 1400-2400 UTC
Interesting points are those below the 1:1 line since they have significant curvature
Run with FDDA and 1-h SST Correlates well with
measured wind (r > 0.9) in either run with FDDA
Non-FDDA run not as good (r < 0.85)
New metrics:Vector average wind
Good correlation with max ozone from airborne measurements
r = -0.91, r2 = 0.83 Run with FDDA and 1-h SST Runs without 1-h SST about
the same Without FDDA results are
much worse Scalar speed correlation
slightly worse(?) (r = -0.88) but still better than net trajectory distance
Lagrangian plume comparisons
FLEXPART dispersion model with real emissions
Met fields from WRF (red) and ECMWF (blue)
SO2 measurements from NOAA aircraft (black)
WRF result has much better resolution and plume locations, even if averaged to same grid
Conclusions ECMWF model used for initialization is already quite good, making it difficult to
demonstrate improvement with high-resolution simulations Traditional statistics (bias and std. dev.) don’t crisply display differences
between runs, although they generally indicate improvement with FDDA– Different sites show different results
Looking at distribution of errors is useful– Large errors in temperature (>5K) occur when moist convection is present
New metric of sea breeze correspondence shows improvement at all 7 surface sites with FDDA
Net trajectory distance correlates better with ozone than total distance Vector average wind correlates still better with ozone, scalar average wind
speed almost as good Average wind (vector or scalar) shows clearly that FDDA makes an important
improvement under high-ozone conditions Improvement above the surface is easy to demonstrate (eg. by comparison with
wind profiler data) Lagrangian plume model provides clear information about directly relevant
performance of the model, but how to encapsulate? Uncertainty analysis is needed How good is good enough? What if we know we have improved the model, but can’t show that we have
improved the results?
Thanks to:
Bryan Lambeth, Texas Commission on Environmental Quality
NOAA P3 scientistsRichard Pyle and Vaisala, Inc. for
fundingand many others
New metrics:Sea breeze frequency
How often does a sea breeze occur in the simulation or measurement?
Definition: Northerly component >1 m/s between 0600 and 1200 UTC and southerly >1 m/s after 1200 UTC
FDDA or FDDA+1hSST run closer to measurement at 4 of 7 sites Red is FDDA run
Blue has FDDA, 1-h SST, and reduced soil moisture
Green has reduced soil moisture onlyBlack is surface site measurement
New metrics:Stagnation frequency
How often does stagnation occur in the simulation or measurement?
Definition: Wind speed < 1 m/s at any hour between 1500 and 2300 UTC
FDDA or FDDA+1hSST run closer to measurement at 3 of 7 sites
Red is FDDA runBlue has FDDA, 1-h SST, and reduced soil
moistureGreen has reduced soil moisture onlyBlack is surface site measurement
New metrics:Stagnation frequency
How often does stagnation occur in the simulation AND measurement?
Definition: Wind speed < 1 m/s at any hour between 1500 and 2300 UTC
No clear improvement with FDDA or FDDA+1hSST
Results not sensitive to threshold
Red is FDDA runBlue has FDDA, 1-h SST, and reduced soil
moistureGreen has reduced soil moisture only
New metrics:Sea breeze and stagnation
Other things we can learn from these metrics:– Sea breeze correspondence
is good at C45, closest to Bay and Gulf, with high frequency
– Even better sea breeze correspondence at C81 with lowest frequency
– C45 has the lowest stagnation frequency
Red is FDDA runBlue has FDDA, 1-h SST, and reduced soil
moistureGreen has reduced soil moisture only