Diurnal Variability of Aerosols Observed by Ground-based Networks Qian Tan (USRA), Mian Chin (GSFC), Jack Summers (EPA), Tom Eck (GSFC), Hongbin Yu (UMD),

Slides:



Advertisements
Similar presentations
David J. Sailor1 and Hongli Fan2 1. Portland State University
Advertisements

NASA AQAST 6th Biannual Meeting January 15-17, 2014 Heather Simon Changes in Spatial and Temporal Ozone Patterns Resulting from Emissions Reductions: Implications.
CO budget and variability over the U.S. using the WRF-Chem regional model Anne Boynard, Gabriele Pfister, David Edwards National Center for Atmospheric.
Cost-effective dynamical downscaling: An illustration of downscaling CESM with the WRF model Jared H. Bowden and Saravanan Arunachalam 11 th Annual CMAS.
Aerosol Daytime Variations over North and South America as Derived from Multiyear AERONET Measurements Yan Zhang 1, Hongbin Yu 2, Alexander Smirnov 1,
Quantifying uncertainties of OMI NO 2 data Implications for air quality applications Bryan Duncan, Yasuko Yoshida, Lok Lamsal, NASA OMI Retrieval Team.
Junwei Xu 1 Randall V. Martin 1,2, Jhoon Kim 3, Myungje Choi 3, Qiang Zhang 4, Guannan Geng 4, Yang Liu 5, Zongwei Ma 5,6, Lei Huang 6, Yuxuan Wang 4,7.
Global Climatology of Fine Particulate Matter Concentrations Estimated from Remote-Sensed Aerosol Optical Depth Aaron van Donkelaar 1, Randall Martin 1,2,
The Averaging Kernel of CO2 Column Measurements by the Orbiting Carbon Observatory (OCO), Its Use in Inverse Modeling, and Comparisons to AIRS, SCIAMACHY,
Satellite-based Global Estimate of Ground-level Fine Particulate Matter Concentrations Aaron van Donkelaar1, Randall Martin1,2, Lok Lamsal1, Chulkyu Lee1.
Human health applications of atmospheric remote sensing Simon Hales, Housing and Health Research Programme, University of Otago, Wellington, New Zealand.
1 Progress Report to MDE June 7, 2010 Dr. Konstantin Vinnikov, Acting State Climatologist for Maryland Prof. Russell Dickerson, Department of Atmospheric.
1 Surface O 3 over Beijing: Constraints from New Surface Observations Yuxuan Wang, Mike B. McElroy, J. William Munger School of Engineering and Applied.
Satellite Remote Sensing of Surface Air Quality
2 nd GEO-CAPE Community Workshop Boulder, CO May 11-13, 2011 Spatio-temporal Variability of Ozone Laminae Michael J. Newchurch 1, Guanyu Huang 1, John.
1 Satellite Remote Sensing of Particulate Matter Air Quality ARSET Applied Remote Sensing Education and Training A project of NASA Applied Sciences Pawan.
Tropospheric Ozone Laminar Structures and Vertical Correlation Lengths Michael J. Newchurch 1, Guanyu Huang 1, Brad Pierce 3, John Burris 2, Shi Kuang.
Visualization, Exploration, and Model Comparison of NASA Air Quality Remote Sensing data via Giovanni Ana I. Prados, Gregory Leptoukh, Arun Gopalan, and.
1 Satellite Remote Sensing of Particulate Matter Air Quality ARSET Applied Remote Sensing Education and Training A project of NASA Applied Sciences Pawan.
Investigation of Decadal Changes in Aerosol and Asthma Sponsors: National Aeronautics and Space Administration (NASA) NASA Goddard Space Flight Center.
Application of Satellite Data to Particulate, Smoke and Dust Monitoring Spring 2015 ARSET - AQ Applied Remote Sensing Education and Training – Air Quality.
Training Workshop in Partnership with BAAQMD
Chapter 4: How Satellite Data Complement Ground-Based Monitor Data 3:15 – 3:45.
Transport of Asian Dust to the Mid-Atlantic United States: Lidar, satellite observations and PM 2.5 speciation. Rubén Delgado, Sergio DeSouza-Machado Joint.
Developing a High Spatial Resolution Aerosol Optical Depth Product Using MODIS Data to Evaluate Aerosol During Large Wildfire Events STI-5701 Jennifer.
Page1 PAGE 1 The influence of MM5 nudging schemes on CMAQ simulations of benzo(a)pyrene concentrations and depositions in Europe Volker Matthias, GKSS.
1 Satellite Remote Sensing of Particulate Matter Air Quality ARSET Applied Remote Sensing Education and Training A project of NASA Applied Sciences Pawan.
Advances in Applying Satellite Remote Sensing to the AQHI Randall Martin, Dalhousie and Harvard-Smithsonian Aaron van Donkelaar, Akhila Padmanabhan, Dalhousie.
GOES and GOES-R ABI Aerosol Optical Depth (AOD) Validation Shobha Kondragunta and Istvan Laszlo (NOAA/NESDIS/STAR), Chuanyu Xu (IMSG), Pubu Ciren (Riverside.
1 Satellite Remote Sensing of Particulate Matter Air Quality ARSET-AQ Applied Remote SEnsing Training A project of NASA Applied Sciences Pawan Gupta Originally.
Assessment of aerosol plume dispersion products and their usefulness to improve models between satellite aerosol retrieval and surface PM2.5  Chowdhury.
P. K. Patra*, R. M. Law, W. Peters, C. Rodenbeck et al. *Frontier Research Center for Global Change/JAMSTEC Yokohama, Japan.
Model Evaluation Comparing Model Output to Ambient Data Christian Seigneur AER San Ramon, California.
1 Satellite Remote Sensing of Particulate Matter Air Quality ARSET Applied Remote SEnsing Training A project of NASA Applied Sciences Pawan Gupta Satellite.
Clare Flynn, Melanie Follette-Cook, Kenneth Pickering, Christopher Loughner, James Crawford, Andrew Weinheimer, Glenn Diskin October 6, 2015 Evaluation.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
NATURAL AND TRANSBOUNDARY POLLUTION INFLUENCES ON AEROSOL CONCENTRATIONS AND VISIBILITY DEGRADATION IN THE UNITED STATES Rokjin J. Park, Daniel J. Jacob,
Investigations of Artifacts in the ISCCP Datasets William B. Rossow July 2006.
Validation of OMI NO 2 data using ground-based spectrometric NO 2 measurements at Zvenigorod, Russia A.N. Gruzdev and A.S. Elokhov A.M. Obukhov Institute.
Introduction 1. Advantages and difficulties related to the use of optical data 2. Aerosol retrieval and comparison methodology 3. Results of the comparison.
Satellite Basics MAC Smog Blog Training CATHALAC, Panama, Sept 11-12, 2008 Jill Engel-Cox & Erica Zell Battelle Memorial Institute
Evaluation of OMI total column ozone with four different algorithms SAO OE, NASA TOMS, KNMI OE/DOAS Juseon Bak 1, Jae H. Kim 1, Xiong Liu 2 1 Pusan National.
Shaocheng Xie, Renata McCoy, and Stephen Klein Lawrence Livermore National Laboratory Statistical Characteristics of Clouds Observed at the ARM SGP, NSA,
Summary of recent progress in GEO-CAPE aerosol related study GEO-CAPE aerosol working group Contributions from: Shana Mattoo, Lorraine Remer, Yan Zhang,
Improving MISR-retrieved Aerosol Properties Using GOCART Simulations Yang Liu, PhD June 3, 2015 St. Louis, MO.
Evaluating temporal and spatial O 3 and PM 2.5 patterns simulated during an annual CMAQ application over the continental U.S. Evaluating temporal and spatial.
Impact of the changes of prescribed fire emissions on regional air quality from 2002 to 2050 in the southeastern United States Tao Zeng 1,3, Yuhang Wang.
Estimating PM 2.5 from MODIS and MISR AOD Aaron van Donkelaar and Randall Martin March 2009.
Some Applications of Satellite Remote Sensing for Air Quality: Implications for a Geostationary Constellation Randall Martin, Dalhousie and Harvard-Smithsonian.
Dust aerosols in NU-WRF – background and current status Mian Chin, Dongchul Kim, Zhining Tao.
INTEGRATING SATELLITE AND MONITORING DATA TO RETROSPECTIVELY ESTIMATE MONTHLY PM 2.5 CONCENTRATIONS IN THE EASTERN U.S. Christopher J. Paciorek 1 and Yang.
Chemical Data Assimilation: Aerosols - Data Sources, availability and needs Raymond Hoff Physics Department/JCET UMBC.
Review of PM2.5/AOD Relationships
Impact of Temporal Fluctuations in Power Plant Emissions on Air Quality Forecasts Prakash Doraiswamy 1, Christian Hogrefe 1,2, Eric Zalewsky 2, Winston.
Geostationary satellite mission for air quality and coastal ecosystems One of 15 missions recommended to NASA for the next decade by the U.S. National.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Aerosol Pattern over Southern North America Tropospheric Aerosols: Science and Decisions in an International Community A NARSTO Technical Symposium on.
Long-term measurements of surface ozone at remote and rural sites in China Xiaobin Xu 1, Weili Lin 1,2 1 Chinese Academy of Meteorological Sciences Key.
Background ozone in surface air over the United States Arlene M. Fiore Daniel J. Jacob US EPA Workshop on Developing Criteria for the Chemistry and Physics.
LAND TEAM. GOES-R AWG Annual Meeting. June 14-16, 2011
Adverse Effects of Drought on Air Quality in the US
Daytime variations of AOD and PM2
Presentation by: Dan Goldberg1
A Novel Approach for Identifying Dust Storms with Hourly Surface Air Monitors in the Western United States Barry Baker1,2 and Daniel Tong1,2 1National.
A Multi-angle Aerosol Optical Depth Retrieval Algorithm for GOES
A Discussion on TEMPO Draft CH2O Validation Plan
LAND TEAM. GOES-R AWG Annual Meeting. June 14-16, 2011
Satellite Remote Sensing of Ground-Level NO2 for New Brunswick
LAND TEAM. GOES-R AWG Annual Meeting. June 14-16, 2011
Ming-Dah Chou Department of Atmospheric Sciences
Presentation transcript:

Diurnal Variability of Aerosols Observed by Ground-based Networks Qian Tan (USRA), Mian Chin (GSFC), Jack Summers (EPA), Tom Eck (GSFC), Hongbin Yu (UMD), Caterina Tassone (NOAA), Yan Zhang (MSU), EPA/AQS, NASA/AERONET, NOAA/NCDC

Outline  Diurnal variability of surface PM2.5  How significant  Variations on other time scales.  Linkage between diurnal cycle of surface PM2.5 and column AOT  Correlation on their diurnal cycles  Possible meteorological impacts

Measuring Aerosol Variations in Different Ways Day 1Day 2Day 3Day 4Day 5………Day n Day-to-day variation (EPA 24-hr filter) Sun-synchronized orbit Better spatial coverage Geo-stationary orbit EPA hourly obs.

Aerosols Diurnal Variation  Continuous ground based observations.  EPA AQS hourly PM2.5 observations.  Diurnal variation vs daily average  Comparison to seasonal variations.

Averaged PM 2.5 Diurnal Variations PM 2.5 (ug/m^3) Max-Min Std. Dev Significant diurnal variation is observed: ~ ug/m 3, EPA PM2.5 standard: 35 ug/m 3 for 24hr, 15 ug/m 3 annual average.

Compared with Daily Average Percentage (%) (Max-Min) / Mean Std. Dev/ Mean Variations of surface PM2.5 within a day is comparable to its daily mean: Maximum-minimum is % of its mean Standard deviation is ~30-50%

Seasonal & Year-Year Difference Max-Min Std Dev On average, the standard deviation of PM2.5 within a day is comparable to the seasonal variation.

Co-located PM2.5 and AOT  Using column AOT, i.e. what satellites observe, to estimate the surface concentration of PM2.5 (criteria pollutant)  Chu et al., (2003), Wang & Christopher (2003), Engel-Cox (2004), Al-Saadi et al., (2005),…, Hoff & Christopher (2009)  Co-located AERONET and AQS observations  New York City (CCNY)  Baltimore (MD Science Center)  Houston (University of Houston)  Fresno (California) Within 8km. Hourly data available Close by hourly meteorological & PBL observations

Day-to-Day PM2.5 vs AOT On daily based, AOT shows good correspondence with surface PM2.5 concentration. Their correlation has large spatial differences (both r 2 and slope).

Diurnal Cycle of PM2.5 & AOT -- Houston PM2.5 shows clearer diurnal pattern, it changes with season. AOT diurnal pattern is less pronounced, larger seasonal variation Daily PM2.5 minimum is at noon time during fall and winter.

Correlation between AOT and PM2.5 on finer temporal frequency Koelemeijer et al., 2006; Hoff & Christopher (2009) Causes of variations PM2.5 emissions, chemistry, deposition, dynamics, … AOT all of above aerosol optical property composition size and shape aerosol vertical profile PBL local, regional, and long range transport other factors clouds, (surface albedo) solar zenith angle

Diurnal Variation of PBL PBL peaks in the early afternoon PBL is higher in summer (in Houston, less seasonal difference)

PBL vs. PM2.5 Houston Baltimore New York City Winter In winter, if PBL is high, then PM2.5 will be low -- in Houston, the minimum PM2.5 occurred around noon time.

AOT vs. PM 2.5 * PBL R 2 = 0.39 (2010) R 2 =0.26 When PBL is high (>1000m), AOT is more correlated with PM2.5 When PBL is high (>1000m), AOT is more correlated with PM2.5 R 2 = PBL > 1000m

AOT vs PM2.5 * PBL *f(RH) R 2 = 0.17 R 2 = 0.40 R 2 = * F (RH) R 2 = 0.42 All PBL condition PBL >1000m + surface RH 1.Low PBL will degrade correlation between AOT and PM2.5 2.When PBL is high, it is more likely to estimate PM2.5 using AOT.

Conclusion  Significant daily variation is observed in surface PM2.5 concentration.  Daily average of PM2.5 and AOT is correlated well at urban sites.  Diurnal cycle of PM2.5 and AOT is different.  better correlated when PBL is high

Extra slides

Diurnal Cycle of PM2.5 and AOT -- NYC PM2.5 diurnal variation follow emission (traffic) pattern, & PBL AOT diurnal pattern is less pronounced, large seasonal variation No clear pattern in summer months.

Correlation between AOT and PM2.5  Many studies to explore the linkage between the two  Using column AOT, i.e. what satellite can observe, to estimate the surface concentration of PM2.5 (criteria pollutant)  Chu et al., (2003), Wang & Christopher (2003), Engel-Cox (2004), Al-Saadi et al., (2005),…, Hoff & Christopher (2009)