spatial variability of trace gases during discover-aq ... for geostationary observations of...

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Spatial Variability of Trace Gases during DISCOVER-AQ: Planning for Geostationary Observations of Atmospheric Composition A11G - 0132 Melanie B. Follette-Cook 1,2 , K. Pickering 2 , J. Crawford 3 , W. Appel 4 , G. Diskin 3 , A. Fried 5 , C. Loughner 6 , G. Pfister 7 , A. Weinheimer 8 1 Morgan State University/GESTAR; 2 NASA GSFC, 3 NASA LARC, 4 EPA, 5 Univ. of Colorado, 6 ESSIC/UMD, 7 UCAR, 8 NCAR [email protected] The Tropospheric Emissions: Monitoring of Pollution (TEMPO) instrument will be the first NASA mission to make atmospheric composition observations from geostationary orbit and partially fulfills the goals of the Geostationary Coastal and Air Pollution Events (GEO-CAPE) mission Follette-Cook et al. (2015, Atmos. Environ.) related observed and simulated variability to the precision requirements defined by the science traceability matrices of these space-borne missions In that work, we quantified the spatial and temporal variability of column integrated and in-situ observations of trace gases over the Baltimore/Washington, DC area using output from WRF/Chem for the entire month of July 2011, coinciding with the first deployment of the NASA Earth Venture program mission DISCOVER-AQ (Deriving Information on Surface conditions from Column and Vertically Resolved Observations Relevant to Air Quality) Here, we expand that analysis to include the other three deployments of DISCOVER-AQ Motivation Structure Functions Structure functions are a useful way to quantify variability in both space and time • < > = the average of data pairs separated by distance y • Z = variable of interest at given location x • q = scaling exponent (here q =1) ƒ(Z, y)<Z(x + y) - Z(x) q > Calculate structure functions using data from DISCOVER-AQ P- 3B in-situ aircraft (14 flights for MD) Criteria: - Both points must be below 2 km (AGL) - The points must be < 2 hrs apart (1.75 hrs for MD) - The 1-second merge data was used for this analysis - Model output was sampled along the P-3B flight track Maryland Analysis Highlights – Follette-Cook et al. (2015) Follette-Cook et al. (2015) quantified the variability seen in the Maryland/DC DISCOVER-AQ P-3B trace gas data and found it compared well with our WRF/Chem simulation Questions addressed in that analysis: Precision Requirements (PR) for GEO-CAPE/TEMPO TEMPO spatial resolution: 8x4.5 km * calculated quantity ** Lok Lamsal, personal communication Species Altitude range STM Precision Temporal Revisit O 3 0-2 km 10 ppbv 1.7 DU* 2 hr O 3 Tropospheric column 10 ppbv 6.2 DU* 1 hr CO 0-2 km 20 ppbv 0.91x10 17 molec/cm 2 * 1 hr CO 2 km - tropopause 20 ppbv 2.5x10 17 molec/cm 2 * 1 hr CO Tropospheric column 3.4x10 17 molec/cm 2 * 1 hr NO 2 Tropospheric column 1x10 15 molec/cm 2 ~1 ppbv** 1 hr HCHO Tropospheric column 1x10 16 molec/cm 2 3 hr SO 2 Tropospheric column 1x10 16 molec/cm 2 3 hr How much does each species vary spatially and temporally throughout the campaign? (i.e. one month) How much of that variability would a TEMPO-like instrument see? Is the resolvable variability sufficient answer the relevant science questions? Percentiles of observed and simulated differences 14 flights - July 2011 Ozone WRF/Chem P-3B 25 th 50 th 75 th 85 th 95 th Mean WRF/Chem – P-3B Percentiles 14 flights - July 2011 O 3 HCHO CO NO 2 WRF/Chem reproduces the variability in O 3 well Slightly overestimates the variability of CO and NO 2 Underestimates the variability in HCHO Can WRF/Chem capture the variability seen in the MD DISCOVER-AQ observations? NO 2 (trop column) HCHO (trop column) What is the geographic coverage of observable differences? O 3 (0-2 km) 4 km model field Gridcell to gridcell differences, 4-8 km apart, larger than PR Gridcell to gridcell differences, 20- 24 km apart, larger than PR Gridcell to gridcell differences, 36- 40 km apart, larger than PR CO (0–2 km) These results indicate that the TEMPO instrument would be able to observe O 3 air quality events over the Mid-Atlantic area, even on days when the violations of the air quality standard are not widespread. 7/29/2011 2 pm EDT – “Code Orange” Day (8-hr max O3 between 76 and 95 ppbv) The maximum differences in NO 2 are in the morning and early evening, so 2 pm represents a minimum in what would be observable Despite that, the major features in the tropospheric column field can be seen in the plot of the visible differences at 4 – 8 km distances In MD, sources of HCHO include oxidation of hydrocarbons with both biogenic and anthropogenic sources. Thus, greater variability in HCHO is seen at longer distances, i.e. greater than 20 km, and would be hypothetically resolvable by TEMPO DISCOVER-AQ observations and simulations Maryland – Jul 2011 California Jan/Feb 2013 Texas – Sep 2013 Colorado Jul/Aug 2014 Campaign flight paths Objective: Characterize the relationship between air quality at the surface and in the tropospheric columns that can be measured from a satellite Observing strategy: Concurrent in-situ and remote sensing observations from a network of ground sites and two research aircraft Simulations: Maryland – Follette-Cook et al. (2015) WRF/Chem v3.3.1 – 4 km California – W. Appel Coupled WRF/CMAQ v5.0.2 – 4 km Houston – C. Loughner WRF/CMAQ v5.0.2– 4 km Colorado – G. Pfister WRF/Chem – 3 km How well do models capture the variability seen in the DISCOVER-AQ observations? 25 th 50 th 75 th 85 th 95 th Mean Results from an in-depth analysis of trace gas variability in MD indicated that the variability in this region was large enough to be observable by a TEMPO-like instrument The variability observed in MD is relatively similar to the other three campaigns with a few exceptions: CO variability in CA was much higher than in the other regions; HCHO variability in CA and CO was much lower; MD showed the lowest variability in NO2 All model simulations do a reasonable job simulating O 3 variability. For CO, the CA/CO simulations largely under/overestimate the variability in the observations. The variability in HCHO is underestimated for every campaign. NO2 variability is slightly overestimated in MD, more so in CO. The TX simulation underestimates the variability in each trace gas. This is most likely due to missing emissions sources (C. Loughner, manuscript in preparation). Future Work: Where reasonable, we will use these model outputs to further explore the resolvability from space of these key trace gases using analyses of tropospheric column amounts relative to satellite precision requirements, similar to Follette-Cook et al. (2015). Inter-Campaign Variability The results from the MD analysis suggest that the PRs for TEMPO and GEO-CAPE are sufficient for addressing the science questions they are tasked to answer How does the variability seen in the other three deployments compare to that seen in MD? O 3 – TX, CO, and MD show comparable differences to MD. Air quality events in these regions will likely be observable by TEMPO CO – Variability of all campaigns similar, except for CA, which was much larger NO2 – MD shows the lowest variability of any campaign, and the variability during the MD campaign was large enough to be well-resolved by TEMPO. Therefore, with respect to variability, TEMPO’s NO 2 PR is more than sufficient for these other regions as well. HCHO – MD and TX show largest differences. In MD, larger differences in HCHO are seen at longer distances (> 20 km) and would be hypothetically resolvable by TEMPO. These results indicate that HCHO variability in the San Joaquin Valley and Denver, CO regions might be too small to be resolvable at ~20 km distances. MD CA TX CO CO HCHO Ozone 25 th percentile Median 75 th percentile 95 th percentile NO 2 Precision Requirement O 3 HCHO CO NO 2 Maryland (14 flights) California (8 out of 12 flights) O 3 HCHO CO NO 2 Texas (9 flights) O 3 HCHO CO NO 2 Colorado (22 flights) O 3 HCHO CO NO 2 Model – P-3B Percentiles Conclusions https://ntrs.nasa.gov/search.jsp?R=20150023592 2018-07-09T00:55:13+00:00Z

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Page 1: Spatial Variability of Trace Gases during DISCOVER-AQ ... for Geostationary Observations of Atmospheric Composition A11G - 0132 ... DC area using output from WRF/Chem for the entire

Spatial Variability of Trace Gases during DISCOVER-AQ: Planning for Geostationary Observations of Atmospheric Composition

A11G - 0132

Melanie B. Follette-Cook1,2, K. Pickering2, J. Crawford3, W. Appel4, G. Diskin3, A. Fried5, C. Loughner6, G. Pfister7, A. Weinheimer8 1 Morgan State University/GESTAR; 2 NASA GSFC, 3 NASA LARC, 4 EPA, 5 Univ. of Colorado, 6 ESSIC/UMD, 7 UCAR, 8 NCAR [email protected]

The Tropospheric Emissions: Monitoring of Pollution (TEMPO) instrument will be the first NASA mission to make atmospheric composition observations from geostationary orbit and partially fulfills the goals of the Geostationary Coastal and Air Pollution

Events (GEO-CAPE) mission

Follette-Cook et al. (2015, Atmos. Environ.) related observed and simulated variability to the precision requirements defined by the science traceability matrices of these space-borne missions

In that work, we quantified the spatial and temporal variability of column integrated and in-situ observations of trace gases over the Baltimore/Washington, DC area using output from WRF/Chem for the entire month of July 2011, coinciding with the first deployment of the NASA Earth Venture program mission DISCOVER-AQ (Deriving Information on Surface conditions from

Column and Vertically Resolved Observations Relevant to Air Quality)

Here, we expand that analysis to include the other three deployments of DISCOVER-AQ

Motivation

Structure Functions Structure functions are a useful way to quantify

variability in both space and time

• < > = the average of data pairs separated by distance y • Z = variable of interest at given location x • q = scaling exponent (here q =1)

ƒ(Z, y)≡<Z(x + y) - Z(x)q>

Calculate structure functions using data from DISCOVER-AQ P-3B in-situ aircraft (14 flights for MD) Criteria: - Both points must be below 2 km (AGL) - The points must be < 2 hrs apart (1.75 hrs for MD) - The 1-second merge data was used for this analysis - Model output was sampled along the P-3B flight track

Maryland Analysis Highlights – Follette-Cook et al. (2015) Follette-Cook et al. (2015) quantified the variability seen in the Maryland/DC DISCOVER-AQ P-3B trace gas data and found it compared well with our WRF/Chem simulation Questions addressed in that analysis:

Precision Requirements (PR) for GEO-CAPE/TEMPO

TEMPO spatial resolution: 8x4.5 km * calculated quantity ** Lok Lamsal, personal communication

Species Altitude range STM Precision Temporal Revisit O3 0-2 km 10 ppbv 1.7 DU* 2 hr

O3 Tropospheric column 10 ppbv 6.2 DU* 1 hr CO 0-2 km 20 ppbv 0.91x1017 molec/cm2* 1 hr CO 2 km - tropopause 20 ppbv 2.5x1017 molec/cm2* 1 hr CO Tropospheric column 3.4x1017 molec/cm2* 1 hr NO2 Tropospheric column 1x1015 molec/cm2 ~1 ppbv** 1 hr

HCHO Tropospheric column 1x1016 molec/cm2 3 hr SO2 Tropospheric column 1x1016 molec/cm2 3 hr

• How much does each species vary spatially and temporally throughout the campaign? (i.e. one month)

• How much of that variability would a TEMPO-like instrument see? • Is the resolvable variability sufficient answer the relevant science questions?

Percentiles of observed and simulated differences 14 flights - July 2011 Ozone

WRF/Chem

P-3B

25th 50th 75th 85th 95th Mean

WRF/Chem – P-3B Percentiles 14 flights - July 2011

O3

HCHO

CO

NO2

• WRF/Chem reproduces the variability in O3 well

• Slightly overestimates the variability of CO and NO2

• Underestimates the variability in HCHO

Can WRF/Chem capture the variability seen in the MD DISCOVER-AQ observations?

NO2 (trop column) HCHO (trop column)

What is the geographic coverage of observable differences?

O3 (0-2 km)

4 km model field

Gridcell to gridcell differences, 4-8 km apart, larger than PR

Gridcell to gridcell

differences, 20-24 km apart,

larger than PR

Gridcell to gridcell differences, 36-40 km apart, larger than PR

CO (0–2 km)

These results indicate that the TEMPO instrument would be able to observe O3 air quality events over the Mid-Atlantic area, even on days when the violations of the air quality standard are not widespread.

7/29/2011 2 pm EDT – “Code Orange” Day (8-hr max O3 between 76 and 95 ppbv)

• The maximum differences in NO2 are in the morning and early evening, so 2 pm represents a minimum in what would be observable

• Despite that, the major features in the tropospheric column field can be seen in the plot of the visible differences at 4 – 8 km distances

In MD, sources of HCHO include oxidation of hydrocarbons with both biogenic and anthropogenic sources. Thus, greater variability in HCHO is seen at longer distances, i.e. greater than 20 km, and would be hypothetically resolvable by TEMPO

DISCOVER-AQ observations and simulations

Maryland – Jul 2011 California Jan/Feb 2013

Texas – Sep 2013 Colorado Jul/Aug 2014

Campaign flight paths

Objective: Characterize the relationship between air quality at the surface and in the tropospheric columns that can be measured from a satellite

Observing strategy: Concurrent in-situ and remote sensing observations from a network of ground sites and two research aircraft

Simulations: • Maryland – Follette-Cook et

al. (2015) • WRF/Chem v3.3.1 – 4 km

• California – W. Appel • Coupled WRF/CMAQ v5.0.2

– 4 km • Houston – C. Loughner

• WRF/CMAQ v5.0.2– 4 km • Colorado – G. Pfister

• WRF/Chem – 3 km

How well do models capture the variability seen in the DISCOVER-AQ observations?

25th 50th 75th 85th 95th Mean

• Results from an in-depth analysis of trace gas variability in MD indicated that the variability in this region was large enough to be observable by a TEMPO-like instrument

• The variability observed in MD is relatively similar to the other three campaigns with a few exceptions: • CO variability in CA was much higher than in the other regions; HCHO variability in CA and CO was much lower; MD showed the lowest

variability in NO2 • All model simulations do a reasonable job simulating O3 variability. For CO, the CA/CO simulations largely under/overestimate the variability in the observations. The variability in HCHO is underestimated for every campaign. NO2 variability is slightly overestimated in MD, more so in CO. The TX simulation underestimates the variability in each trace gas. This is most likely due to missing emissions sources (C. Loughner, manuscript in preparation).

• Future Work: Where reasonable, we will use these model outputs to further explore the resolvability from space of these key trace gases using analyses of tropospheric column amounts relative to satellite precision requirements, similar to Follette-Cook et al. (2015).

Inter-Campaign Variability The results from the MD analysis suggest that the PRs for TEMPO and GEO-CAPE are sufficient for addressing the

science questions they are tasked to answer

How does the variability seen in the other three deployments compare to that seen in MD?

O3 – TX, CO, and MD show comparable differences to MD. Air quality events in these regions will likely be observable by TEMPO

CO – Variability of all campaigns similar, except for CA, which was much larger

NO2 – MD shows the lowest variability of any campaign, and the variability during the MD campaign was large enough to be well-resolved by TEMPO. Therefore, with respect to variability, TEMPO’s NO2 PR is more than sufficient for these other regions as well.

HCHO – MD and TX show largest differences. In MD, larger differences in HCHO are seen at longer distances (> 20 km) and would be hypothetically resolvable by TEMPO. These results indicate that HCHO variability in the San Joaquin Valley and Denver, CO regions might be too small to be resolvable at ~20 km distances.

MD

CA

TX

CO

CO

HCHO

Ozone 25th percentile Median

75th percentile

95th percentile

NO2 Precision Requirement

O3

HCHO

CO

NO2

Maryland (14 flights) California (8 out of 12 flights) O3

HCHO

CO

NO2

Texas (9 flights) O3

HCHO

CO

NO2

Colorado (22 flights) O3

HCHO

CO

NO2

Model – P-3B Percentiles

Conclusions

https://ntrs.nasa.gov/search.jsp?R=20150023592 2018-07-09T00:55:13+00:00Z