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This research focuses on enhancing the detection of water vapor trends in the upper troposphere using Raman lidar techniques. Correcting systematic biases and temperature-dependent factors results in more accurate measurements for trend monitoring purposes.
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Techniques for Improving Water Vapor Trend Detection Using Raman LidarD. N. Whiteman, Code 612, NASA GSFC, D. Venable, Howard University, K. Vermeesch, 612/SSAI, I. Veselovskii, 612/GESTAR, M. Cadirola, 612/Ecotronics, L. Oman, 614, E. Weatherhead, CIRES Atmospheric water vapor amounts are anticipated to increase due to increasing atmospheric temperatures related to climate change. Two international networks are using Raman lidar as one of the techniques for monitoring atmospheric water vapor trends. Our recent research indicates: • To improve detection of trends in upper tropospheric (UT) water vapor, it is much more important to increase the frequency of measurement than to decrease the uncertainty of measurements. • This result implies that Raman water vapor lidar is a viable tool for UT trend detection There are two sources of systematic bias that significantly influence Raman water vapor lidar data and need correction with high accuracy: • A common wet bias that is observed in the UT and lower stratosphere • The temperature dependence of the Raman water vapor spectrum which introduces an altitude dependent bias in the Raman lidar water vapor measurements Implementation of the published corrections increases the accuracy of upper tropospheric Raman lidar water vapor measurements making them suitable for atmospheric trend detection purposes. Figure 1: Profile (left) and normalized difference (right) comparisons of MLS and two versions of corrected ALVICE Raman water vapor lidar data. The red version of the corrected ALVICE data is based on comparison with frostpoint hygrometer data which involves expensive launches. The green version of the correction is based on lower stratospheric climatology from MLS, agrees within 10% of the frostpoint-based correction technique and can be used wherever MLS data are available. The MLS climatology (black) and FP (blue) data are shown for comparison. Figure 2: The temperature dependent factor of the Raman lidar equation is shown. New experimental techniques permit this factor to be calculated with total uncertainty of less than 0.5%. The plot at left shows the factor, called FH(T), for the standard atmosphere temperature and illustrates that an uncertainty in the atmospheric temperature of +/- 5K introduces less than a 0.4% uncertainty in the value of the correction. Earth Sciences Division - Atmospheres
Name: David N. Whiteman, NASA/GSFC, Code 612 E-mail: david.n.whiteman@nasa.gov Phone: 301-614-6703 References: • Whiteman, D. N., Demetrius D. Venable, Monique Walker, Martin Cadirola,Tetsu Sakai, Igor Veselovskii: Assessing the temperature dependence of narrow-band Raman water vapor lidar measurements – A practical approach, Applied Optics, 52, 5376–5384, 2013. • Whiteman, D. N., Cadirola, M., Venable, D., Calhoun, M., Miloshevich, L., Vermeesch, K., Twigg, L., Dirisu, A., Hurst, D., Hall, E., Jordan, A., and Vömel, H.: Correction technique for Raman water vapor lidar signal-dependent bias and suitability for water vapor trend monitoring in the upper troposphere, Atmospheric Measurement Techniques, 5, 2893-2916, doi:10.5194/amt-5-2893-2012, 2012. • Whiteman, D. N., K. C. Vermeesch, L. D. Oman, and E. C. Weatherhead , The relative importance of random error and observation frequency in detecting trends in upper tropospheric water vapor, Journal of Geophysical Research, 116, D21118, doi:10.1029/2011JD016610, 2011. Data Sources: Data sources used include NASA/GSFC Raman lidar, NASA/JPL Raman lidar, NASA Microwave Limb Sounder, GEOS-5 Climate Model, NOAA frostpoint hygrometer, Cryogenic Frostpoint Hygrometer, DOE/ARM radiosonde. Technical Description of Figures: Figure 1: Whiteman et al. (2012) found that wet biases were commonly found in upper altitude Raman lidar water vapor data. This figure shows two methods of correction for a wet bias that was present in the NASA/GSFC Atmospheric Lidar for Validation, Interagency Collaboration and Education (ALVICE) lidar system as it operated during the Measurements of Humidity and Validation Experiment (MOHAVE)-2009 campaign held at the Table Mountain Facility of JPL in California. The first method of correction, shown in red and labeled ALV, requires simultaneously launched frostpoint hygrometer instruments. This is a time-consuming and expensive technique but provides high accuracy for the correction. The alternate correction developed in the cited reference relies on lower stratospheric climatology from MLS and provides a correction that agrees with the FP based one to better than 10% from 10–20 km and increases the uncertainty of upper tropospheric measurements at 250 hPa by only 4%. This increase in uncertainty is insignificant based on Whiteman et al (2013). The use of climatology for correcting upper tropospheric Raman lidar water vapor measurements offers a technique that can be implemented at any location without the need to launch frostpoint hygrometers. Corrected Raman lidar water vapor data are found to be suitable to upper tropospheric trend detection. Figure 2: Whiteman et al. (2011) provides a practical method for correcting for the temperature dependence of Raman lidar water vapor measurements. The method is straightforward to implement and yields a correction that is significantly more accurate than a correction based on standard laboratory techniques. Now a known component of the systematic error budget of Raman water vapor lidar data can be corrected with no more than 0.5% uncertainty. Scientific significance: As atmospheric temperatures increase due to increasing greenhouse gases, the atmospheric concentration of water vapor is expected to increase as well. These increases have already been reported in the literature. Given that water vapor is a more infra-red active gas than carbon dioxide, this water vapor feedback exerts a larger radiative forcing than CO2 itself. In fact, the IPCC reports that the contribution of water vapor feedbacks to anticipated warming is fully 50% of the total warming due to atmospheric gases. The need to monitor the trend in water vapor is therefore quite high given its high radiative capacity. For this reason both the Network for the Detection of Atmospheric Composition Change (NDACC) and the GCOS Reference Upper Air Network (GRUAN) are tasked with monitoring atmospheric water vapor and are incorporating Raman lidars into their instrumentation suite for this purpose. Reference 1 establishes that the random error characteristics of Raman lidar are well suited to the measurement challenge for detecting atmospheric water vapor. But, in order for Raman lidar to provide measurements of sufficient accuracy for trend detection purposes known systematic errors must be corrected. References 2 and 3 above document necessary corrections for Raman water vapor lidar data. Relevance for Future Missions: This research has provided validation data for the MLS instrument. SMAP, PATH, GEO-CAPE all involve moisture measurement and will benefit from quality water vapor data. Given the importance of atmospheric water vapor in determining IR radiances, all IR sensors require accurate water vapor profiles for radiance and retrieval validation. These measurements are needed also for validating models like GEOS-5. Earth Sciences Division - Atmospheres
Aerosol Observations under Thin Cirrus from MODISJaehwa Lee, N. Christina Hsu, Corey Bettenhausen, and Andrew Sayer Code 613, NASA GSFC Aerosols are tiny particles suspended in the atmosphere and play a significant role in the Earth’s energy budget (e.g. IPCC, 2007). These particles can reflect and absorb solar energy and act as cloud condensation nuclei. Due to their diverse sources (both natural and anthropogenic) and short lifetime (~few days), satellite observations with near or full daily global coverage are a priority for aerosol-climate studies. Among NASA’s Earth Observing System (EOS) satellite instruments, the Moderate Resolution Imaging Spectro-radiometer (MODIS) aboard the Terra and Aqua platforms have been providing information about aerosols over the globe for more than a decade. However, this information has been limited to cloud-free areas, hindering us from seeing more complete picture of aerosols including radiative forcing in the presence of clouds, particularly over Southeast Asia where the frequency of thin cirrus occurrence is as high as 50% (Huang et al., 2013). Recently, we have successfully performed aerosol retrievals under thin cirrus to help mitigate this limitation. The results shown here are only over ocean, but this methodology can also be applied to land areas. The study over land is currently being finalized using Deep Blue algorithm (Hsu et al., 2013). This technique not only substantially recovers the aerosol information under thin cirrus, but also reduce cloud contamination in aerosol retrievals compared to the original algorithm (Lee et al., 2013). This approach can also be applied to other sensors making measurements at similar wavelengths as MODIS. a b c Figure 1: (a) MODIS-retrieved aerosol amount in terms of aerosol optical depth (AOD) without cirrus correction, (b) AOD with cirrus correction, and (c) AOD difference between the two (uncorrected – corrected) off of the coast of Africa on 4 March 2007. A moderate dust event is observed with some areas under cirrus clouds. Black line shows Cloud-Aerosol Lidar with Orthogonal Polarization (CALIOP) observation track. a b c d Figure 2:Seasonal average of (a) AOD-uncorrected, (b) AOD-corrected, (c) AOD-corrected only for cirrus-covered areas, and (d) the difference between (a) and (b) over the “Eastern Tropics” for the period from 1 March 2007 to 31 May 2007. Earth Sciences Division - Atmospheres
Name: Jaehwa Lee, NASA/GSFC, Code 613 and Earth System Science Interdisciplinary Center, University of Maryland, College Park E-mail: jaehwa.lee@nasa.gov Phone: 301-614-6407 References: IPCC (2007), Climate Change 2007: The Physical Science Basis, Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. In: Solomon, S., Qin, D., Manning, M., Chen, Z., Marquis, M., Averyt, K. B., Tignor, M., and Miller, H. L. (Eds.), Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA. Huang, J., N. C. Hsu, S.-C. Tsay, Z. Liu, M.-J. Jeong, R. A. Hansell, and J. Lee (2013), Use of spaceborne lidar for the evaluation of thin cirrus contamination and screening in the Aqua MODIS Collection 5 aerosol products, Journal of Geophysical Research: Atmospheres, 118, doi:10.1002/jgrd.50504. Hsu, N. C.,M.-J. Jeong, C. Bettenhausen, A.M. Sayer, R. Hansell, C. S. Seftor, J. Huang, and S.-C. Tsay (2013), EnhancedDeep Blue aerosol retrieval algorithm: The second generation, Journal of Geophysical Research: Atmospheres, 118, doi:10.1002/jgrd.50712. Lee, J., N. C. Hsu, C. Bettenhausen, and A. M. Sayer (2013), Retrieval of aerosol optical depth under thin cirrus from MODIS: application to an ocean algorithm, Journal of Geophysical Research: Atmospheres, accepted. Data Sources: Aqua/MODIS L1B (MYD021KM) and geolocation (MYD03) data, AERONET level 2 spectral AOD data, CALIOP aerosol layer (CAL_LID_L2_05kmALay) and cloud layer (CAL_LID_L2_05kmCLay) data Technical Description of Figures: Figure 1: To retrieve AOD under thin cirrus cover, we first correct the TOA reflectance for the thin cirrus signal. Since the correction requires cirrus-only reflectance to be subtracted from the observed TOA reflectance, we adopt an empirical method to derive the cirrus-only reflectance from the TOA reflectance at 1.38 mm. The AOD without the cirrus correction procedure shows apparent imprints of thin cirrus contamination around 8oN to 12oN near the CALIOP track, while the cirrus-corrected AOD shows reduced contamination and spatial variability over the same areas. It should be noted that the cirrus correction procedure not only reduces the contamination but also recovers some areas (16oN – 18oN, 20oW – 24oW) which were screened out by the cloud screening procedure. In this case study, the magnitude of the AOD correction is as large as 0.35, demonstrating the strong impact of thin cirrus contamination on AOD. Figure 2: A long-term average of the cirrus-corrected AOD is shown, demonstrating similar spatial pattern with the overall cases, which mainly consist of clear-sky data. The spatial patterns are similar between corrected and uncorrected data including both cirrus-covered and clear-sky data, but the uncorrected AOD, in general, is higher than the corrected AOD by up to 0.02. In some smaller areas, the uncorrected AOD data is lower than the corrected data due to difference in sampling as the cirrus correction recovers some data previously lost due to cloud filtering. Note that the cirrus correction procedure generally reduces the AOD due to the lower TOA reflectance after the correction. Scientific significance: Providing more accurate and complete datasets to the user community is a central role of NASA missions. Recent findings suggest that MODIS-like sensors can provide aerosol information above clouds, and this study adds information below transparent cirrus clouds, which can help to improve our understanding of the radiative forcing of aerosols. Relevance to future science and NASA missions: In addition to the more than ten year time series available from each of the two MODIS sensors, the technique can also be applied to other sensors making measurements at similar wavelengths, such as the Visible and Infrared Imaging Radiometer Suite (VIIRS) aboard the Suomi-National Polar Orbiting Partnership (S-NPP) satellite, launched in late 2011, and similar follow-on missions. Earth Sciences Division - Atmospheres
NO2 pollution Increases Exponentially With Urban Population L.N. Lamsal (GESTAR/614, NASA GSFC), R.V. Martin (Dalhousie University), D.D. Parrish (CSD-ESRL, NOAA), N.A. Krotkov (614, NASA GSFC) Concern is growing about the effects of urbanization on air pollution and health. Nitrogen dioxide (NO2), released primarily from combustion processes, is a short-lived atmospheric pollutant that serves as an air quality indicator, and is itself a health concern. The NO2 data from the Aura Ozone Monitoring Instrument (OMI) are actually “columns”, which is defined as the number of molecules of a gas between the satellite instrument and the Earth’s surface.We used model-simulated vertical distributions of NO2 to derive how much NO2 in the column is near the surface, or “nose-level”. The OMI-derived surface NO2 data are significantly correlated with independent surface measurements. We examined how the OMI-derived nose-level NO2 concentrations, OMI NO2 columns, and bottom-up NOx emission inventories relate to urban population. Surface NO2 is significantly correlated with population for the three countries and one continent examined in this study. Urban NO2 pollution, like other urban properties, is a power law scaling function of the population size: the NO2concentration increases proportionally to population raised to an exponent. The value of the exponent (ß) varies by region (e.g., 0.36 for India to 0.66 for China) reflecting regional differences in industrial development and per capita emissions. Energy efficiency increases and therefore per capita NOx emissions decrease with urban population; here we show how outdoor ambient NO2 concentrations depend on urban population. Figure 1. Annual average afternoon surface NO2 mixing ratios for the year 2005 binned at 0.25ᵒ latitude x 0.25ᵒ longitude from OMI over North America, Europe, China, and India. Contours represent population density data gridded at 0.25ᵒx0.25ᵒ resolution with 100 persons km-2 (pink) and 500 persons km-2 (black). Figure 2. Log-log plot of OMI-derived surface NO2 as a function of urban area population for the United States, Europe, China, and India. The line represents the linear least-square fit to the points. Lamsal L., et al., (2013), EST Earth Sciences Division - Atmospheres
Name: Lok N. Lamsal, GESTAR/NASA GSFC Code 614 • E-mail: Lok.Lamsal@nasa.gov Phone: 301-614-5160 • References: • Bettencourt, L.M.A.; Lobo, J; Helbing D.; Kuehnert, C; West G.B. Growth, innovation, scaling, and the pace of life in cities. PNAS. 2007, 104, 17, 7301-7306. • Lamsal, L.N.; Martin, R.V.; Parrish, D.D.; Krotkov, N.A. Scaling relationship for NO2 pollution and population size: A satellite perspective. Environ. Sci. & Technol. 2013, 47 (14), pp 7855–7861, DOI: 10.1021/es400744g. • Lamsal, L.N.; Martin, R.V.; van Donkelaar, A.; Steinbacher, M.; Celarier, E.A.; Bucsela, E.; Dunlea, E.J.; Pinto, J.P. Ground-level nitrogen dioxide concentrations inferred from the satellite-borne Ozone Monitoring Instrument. J. Geophys. Res. 2008, 113, D16308, doi:10.1029/2007JD009235. • Bucsela, E. J.; Krotkov, N. A.; Celarier, E. A.; Lamsal, L. N.; Swartz, W. H.; Bhartia, P. K.; Boersma, K. F.; Veefkind, J. P.; Gleason, J. F.; Pickering, K. E. A new algorithm for retrieving vertical column NO2 from nadir viewing satellite instruments: Applications to OMI. Atmos. Meas. Tech. 2013, 6, 1361−1407. • Data Sources: Operational OMI tropospheric NO2 column retrievals (v2.1) available from NASA DISC archive at http://disc.sci.gsfc.nasa.gov/Aura/data-holdings/OMI/omno2_v003.shtml. Ground level NO2 concentrations were inferred from OMI tropospheric NO2 columns applying local column-to-surface scaling factor from the GEOS-Chem model. Population density data were obtained from the Center for International Earth Science Information Network (CIESIN), Columbia University, http://sedac.ciesin.columbia edu/gpw/. • Technical Description of Figures: • Figure 1:Ground-level NO2 concentrations were derived from OMI tropospheric NO2 retrievals (standard product , v2.1). We followed the approach of Lamsal et al. [2008]that combines simulated local NO2 vertical profile with satellite observations of tropospheric NO2 column. Simulated profiles were taken from the GEOS-Chem model. Population density data are overlaid over the NO2 concentration map. • Figure 2: The relationship between OMI-derived ground-level NO2 mixing ratios and urban population was examined for three countries and a continent: United States, China, India, and Europe. These regions contain two-thirds of total global anthropogenic NOx emissions. We found a significant correlation (r=0.59-71) and a power law scaling relationship between NO2 and urban population. • Relevance for future science/missions: Aura OMI will continue providing NO2 column observations, which can be combined with model information on NO2 vertical distribution to infer “Nose-level” NO2 concentrations. Ground-level NO2 produced primarily from combustion is an air-quality indicator that is associated with respiratory mortality and morbidity. Satellite-derived data provide a unique opportunity to investigate the dependence of ambient air pollutant concentration on urban population, and allow assessing population exposure to air pollution on a global scale. A next generation satellite instruments such as TROPOMI planned for launch by ESA in 2015 as a Sentinel-5 precursor mission and NASA’s Earth Venture Instrument (EVI) Tropospheric Emissions: Monitoring of Pollution (TEMPO) geostationary mission planned for lunch in 2018 will measure NO2 with an increased ground resolution, which will better resolve urban spatial gradient and help examine the scaling relationships at the state/provincial level. The Decadal Survey recommended the Geostationary Coastal and Air Pollution Events (GEO-CAPE) Tier 2 mission which will allow more frequent monitoring of anthropogenic NO2pollution over North and Central America. Earth Sciences Division - Atmospheres