Case Study for Forest Fire Episode

Slides:



Advertisements
Similar presentations
Impacts of BC from fire emission on air quality ---- case study in 2010 Benpei Cao 04/25/13.
Advertisements

Source Apportionment of PM 2.5 in the Southeastern US Sangil Lee 1, Yongtao Hu 1, Michael Chang 2, Karsten Baumann 2, Armistead (Ted) Russell 1 1 School.
FIRE AND BIOFUEL CONTRIBUTIONS TO ANNUAL MEAN AEROSOL MASS CONCENTRATIONS IN THE UNITED STATES ROKJIN J. PARK, DANIEL J. JACOB, JENNIFER A. LOGAN AGU FALL.
Biomass Smoke Aerosol: Spatial and Temporal Pattern over the US October 2005
Fire Modeling issues: fire effects on regional air quality under a changing climate Douglas G. Fox
Air Quality Impacts from Prescribed Burning Karsten Baumann, PhD. Polly Gustafson.
University of Leicester CityZen Contributions
Measurement of the Aerosol Optical Depth in Moscow city, Russia during the wildfire in summer 2010 DAMBAR AIR.
Issues on Ozone Planning in the Western United States Prepared by the WESTAR Planning Committee for the Fall Business Meeting, Tempe, AZ October 31, 2011.
Great Basin Ozone Problem Measurements indicate high ozone concentrations in the Great Basin. Back trajectory analysis and satellite remote sensing will.
NATURAL AND TRANSBOUNDARY INFLUENCES ON PARTICULATE MATTER IN THE UNITED STATES: IMPLICATIONS FOR THE EPA REGIONAL HAZE RULE Rokjin J. Park ACCESS VII,
Go After the Causes What are the principal causes of haze in each area? WRAP emissions WRAP modeling WRAP monitoring (causes of haze) Other studies How.
Reason for Doing Cluster Analysis Identify similar and dissimilar aerosol monitoring sites so that we can test the ability of the Causes of Haze Assessment.
MODELS3 – IMPROVE – PM/FRM: Comparison of Time-Averaged Concentrations R. B. Husar S. R. Falke 1 and B. S. Schichtel 2 Center for Air Pollution Impact.
UC Riverside FEJF Meeting, Las Vegas, NV Dec 8, 2004 UNC/CEPENVIRON Corp. WRAP/RMC Fire Sensitivity Modeling Project Mohammad Omary, Gail Tonnesen WRAP.
Black Carbon Measurements at Whistler Sarah Hanna (UBC)
WRAP COHA Update Seattle, WA May 25, 2006 Jin Xu.
Incorporating Monitoring, Modeling, and EI Data into AoH Analysis AoH Meeting, Salt Lake City September 21-22, 2004 Air Resource Specialists, Inc.
Improved representation of boreal fire emissions for the ICARTT period S. Turquety, D. J. Jacob, J. A. Logan, R. M. Yevich, R. C. Hudman, F. Y. Leung,
UNH Soluble Acidic Gases and Aerosol (SAGA) during INTEX Phase A Jack E. Dibb, Eric Scheuer, and Robert W. Talbot With Thanks to the INTEX Science Team.
Online measurements of chemical composition and size distribution of submicron aerosol particles in east Baltic region Inga Rimšelytė Institute of Physics.
Thanks to David Diner, David Nelson and Yang Chen (JPL) and Ralph Kahn (NASA/Goddard) Research funded by NSF and EPA Overview of the 2002 North American.
Characterization of Emissions In and Near Class I Areas in the West Forum on Sources In and Near Class I Areas.
Influence of the Asian Dust to the Air Quality in US During the spring season, the desert regions in Mongolia and China, especially Gobi desert in Northwest.
Draft, 2 June NATURAL HAZE LEVELS SENSITIVITY ASSESSMENT 1. Project Overview Ivar Tombach Regional Haze Data Analysis Workshop 8 June 2005.
“Quick Look” Trajectory Assessment of Phase 1 Battelle PMF Sources at Lye Brook Wilderness IMPROVE Site P. Wishinski & R. Poirot, VT DEC ° 9 PMF Sources.
Trajectory Calculations Trajectory or backtrajectory analyses use interpolated measured or modeled meteorological fields to estimate the most likely central.
Regional Air Quality Modeling Results for Elemental and Organic Carbon John Vimont, National Park Service WRAP Fire, Carbon, and Dust Workshop Sacramento,
Source Attribution Modeling to Identify Sources of Regional Haze in Western U.S. Class I Areas Gail Tonnesen, EPA Region 8 Pat Brewer, National Park Service.
Renewable Resource Proposals Received by 8/25/00 Overview Presented to the Energy and Environmental.
Weight of Evidence Discussion AoH Meeting – Tempe, AZ November 16/17, 2005.
Implementation Workgroup Meeting December 6, 2006 Attribution of Haze Workgroup’s Monitoring Metrics Document Status: 1)2018 Visibility Projections – Alternative.
Western Air Quality Study (WAQS) Intermountain Data Warehouse (IWDW) Model Performance Evaluation CAMx and CMAQ 2011b University of North Carolina (UNC-IE)
AoH Work Group Weight of Evidence Framework WRAP Meeting – Tucson, AZ January 10/11, 2006 Joe Adlhoch - Air Resource Specialists, Inc.
Sulfate Discussion WRAP Meeting – Tucson, AZ January 10/11, 2006 Joe Adlhoch - Air Resource Specialists, Inc.
Attribution of Haze Project Update Fire Emissions Joint Forum Meeting September 8-9, 2004 Worley, ID.
BACKGROUND AEROSOL IN THE UNITED STATES: NATURAL SOURCES AND TRANSBOUNDARY POLLUTION Daniel J. Jacob and Rokjin J. Park with support from EPRI, EPA/OAQPS.
Revised EPA Ozone Standard – Effects in the West May 15, 2008.
Nitrate Discussion WRAP Meeting – Tucson, AZ January 10/11, 2006 Joe Adlhoch - Air Resource Specialists, Inc.
Yellowstone National Park Very large Class I area (2,219,737 acres) Involves 3 states (WY, ID, MT) Not an isolated wilderness (2.87 million visitors in.
NDVI Active Sensors in Sugarbeet Production for In-Season and Whole Rotation Nitrogen Management.
Colin Michel1, C. Amelynck3, M. Aubinet1, A. Bachy1, P. Delaplace2, A
Status Report to the Stationary Sources Joint Forum:
Review upcoming Teach-Ins and participation in WRAP Regional Haze Planning Work Group - Jay Baker and Tina Suarez-Murias.
The average PM2.5 mass concentration based on IMPROVE data available from September 2000 to December 2002 is 3.3 mg/m3 The highest occurrence of the 20%
Species Specific Reasonable Progress Analysis
Collier County Tourism Research
Svetlana Tsyro, David Simpson, Leonor Tarrason
Contribution of Dust to Regional Haze Based on Available IMPROVE Data From (Provided by Marc Pitchford (NOAA) and Jin Xu (DRI), 01/14/04) Mean.
Evaluating Lower Tropospheric Ozone Simulations Using GOME/SCIAMACHY/OMI Observations of NO2 and HCHO Randall Martin Aaron Van Donkelaar Chris Sioris.
Data from Scott Copeland’s IMPROVE data set
Monitoring VHE Extragalactic Sources with ARGO-YBJ detector
Tom Moore (WESTAR and WRAP) and Pat Brewer (NPS ARD)
Joe Adlhoch - Air Resource Specialists, Inc.
Monitoring Data Sets and Analysis Tools for the VIEWS/TSS Web Sites
Svetlana Tsyro, David Simpson, Leonor Tarrasón
PM2.5 Annual primary standard currently 15 ug/m3
Sources of Haze - North Cascades and Mt. Rainier National Parks
K. Baumann, M.E. Chang, V. Dookwah, S. Lee, A.G. Russell
TAF Regional Haze Plan Update
New CoHA Product Access Page & Representativeness Analysis
Arizona Local (Regional) Dust Episode ?
CAMx-PSAT Source Apportionment Modeling Results
New Approaches to Air Measurements in AOSR
' · · ,.-.., '' !'",. -,..._ ·-.·-...;.· -
Title Why do we underestimate Elemental Carbon in PM?
Reasonable Progress for Additional Class I Areas
Contribution of Dust to Regional Haze Based on Available IMPROVE Data From (Provided by Marc Pitchford (NOAA) and Jin Xu (DRI), 01/14/04) Mean.
Joe Adlhoch - Air Resource Specialists, Inc.
Svetlana Tsyro, David Simpson, Leonor Tarrason
Presentation transcript:

Case Study for Forest Fire Episode 16 Wrap sites 20% worst case days with OC dominant

OC above the 95% Percentile Except REDW1

OC and EC concentrations on July 10 were more than ~50% higher than the average of July 1999. The ratios are similar for the sites in the same region.

From WA and OR

From CA From CA and UT

From UT

From Canada

OC/EC is relatively higher during the forest fire episode

Relationship between nonsoil K and OC/EC on July 10, 1999

OC/EC concentrations are weakly related to the nonsoil K concentrations in BRID (Bridger Wilderness, WY) during the year 1999

Another Episode – Larger Area is Influenced

Relationship between nonsoil K and OC/EC on August 2, 2000

Relatively good correlations have been found between OC/EC concentrations and nonsoil K concentrations in MOZI1 (Mount Zirkel Wilderness, CO) during the year 2000

Summary Forest fire can be regional phenomenon – one fire can influence multiple sites, and one site may be influenced by multiple fire events. OC concentrations on July 10 were more than ~50% higher than the average of July 1999. The increase ratios are similar for the sites in the same region. OC/EC is relatively higher during the forest fire episode – forest fire emits more OC than EC compare with other anthropogenic sources. OC and K concentrations are relatively higher during the forest fire episodes, and some correlation may be found between them. Relatively good correlations have been found between OC/EC concentrations and nonsoil K concentrations in MOZI1 (Mount Zirkel Wilderness, CO) during the year 2000 Try to find measurements of CO – one important indicator of biomass burning, in the surrounding regions.