TEMPLATE DESIGN © 2008 www.PosterPresentations.com A high-order accurate and monotonic advection scheme is used as a local interpolator to redistribute.

Slides:



Advertisements
Similar presentations
Integrated modelling and monitoring for use in forecasting Jørgen Brandt and Finn Palmgren National Environmental Research Institute Department of Atmospheric.
Advertisements

School of something FACULTY OF OTHER School of Computing An Adaptive Numerical Method for Multi- Scale Problems Arising in Phase-field Modelling Peter.
Phoenics User Conference on CFD May 2004 Vipac Engineers & Scientists Ltd COMPUTATIONAL FLUID DYNAMICS Simulation of Turbulent Flows and Pollutant Dispersion.
Use of Lidar Backscatter to Determine the PBL Heights in New York City, NY Jia-Yeong Ku, Chris Hogrefe, Gopal Sistla New York State Department of Environmental.
A numerical simulation of urban and regional meteorology and assessment of its impact on pollution transport A. Starchenko Tomsk State University.
Computational Challenges in Air Pollution Modelling Z. Zlatev National Environmental Research Institute 1. Why air pollution modelling? 2. Major physical.
Introduction to SCREEN3 smokestacks image from Univ. of Waterloo Environmental Sciences Marti Blad NAU College of Engineering and Technology.
Georgia Chapter of the Air & Waste Management Association Annual Conference: Improved Air Quality Modeling for Predicting the Impacts of Controlled Forest.
Georgia Institute of Technology Evaluation of CMAQ with FAQS Episode of August 11 th -20 th, 2000 Yongtao Hu, M. Talat Odman, Maudood Khan and Armistead.
A Cloud Resolving Model with an Adaptive Vertical Grid Roger Marchand and Thomas Ackerman - University of Washington, Joint Institute for the Study of.
The Use of High Resolution Mesoscale Model Fields with the CALPUFF Dispersion Modelling System in Prince George BC Bryan McEwen Master’s project
AIR POLLUTION. ATMOSPHERIC CHEMICAL TRANSPORT MODELS Why models? incomplete information (knowledge) spatial inference = prediction temporal inference.
Spatial Reduction Algorithm for Numerical Modeling of Atmospheric Pollutant Transport Yevgenii Rastigejev, Philippe LeSager Harvard University Michael.
Atmospheric modelling activities inside the Danish AMAP program Jesper H. Christensen NERI-ATMI, Frederiksborgvej Roskilde.
ABSTRACT Many new devices and applications are being created that involve transporting droplets from one place to another. A common method of achieving.
Introduction to the ISC Model Marti Blad NAU College of Engineering.
fluidyn – PANAIR Fluidyn-PANAIR
Georgia Institute of Technology Air Quality Impacts from Prescribed Burning: Fort Benning Case Study M. Talat Odman Georgia Institute of Technology School.
CMAQ (Community Multiscale Air Quality) pollutant Concentration change horizontal advection vertical advection horizontal dispersion vertical diffusion.
CHAPTER 5 Concentration Models: Diffusion Model.
Development of WRF-CMAQ Interface Processor (WCIP)
AMBIENT AIR CONCENTRATION MODELING Types of Pollutant Sources Point Sources e.g., stacks or vents Area Sources e.g., landfills, ponds, storage piles Volume.
Implementation of the Particle & Precursor Tagging Methodology (PPTM) for the CMAQ Modeling System: Mercury Tagging 5 th Annual CMAS Conference Research.
1 Using Hemispheric-CMAQ to Provide Initial and Boundary Conditions for Regional Modeling Joshua S. Fu 1, Xinyi Dong 1, Kan Huang 1, and Carey Jang 2 1.
Supermodel, Supermodel, Can I Breathe Tomorrow? Talat Odman* and Yongtao Hu Georgia Institute of Technology School of Civil & Environmental Engineering.
08/20031 Volcanic Ash Detection and Prediction at the Met Office Helen Champion, Sarah Watkin Derrick Ryall Responsibilities Tools Etna 2002 Future.
Preliminary Study: Direct and Emission-Induced Effects of Global Climate Change on Regional Ozone and Fine Particulate Matter K. Manomaiphiboon 1 *, A.
Source-Specific Forecasting of Air Quality Impacts with Dynamic Emissions Updating & Source Impact Reanalysis Georgia Institute of Technology Yongtao Hu.
4. Atmospheric chemical transport models 4.1 Introduction 4.2 Box model 4.3 Three dimensional atmospheric chemical transport model.
Georgia Institute of Technology Initial Application of the Adaptive Grid Air Quality Model Dr. M. Talat Odman, Maudood N. Khan Georgia Institute of Technology.
Satellite-based inversion of NOx emissions using the adjoint of CMAQ Amir Hakami, John H. Seinfeld (Caltech) Qinbin Li (JPL) Daewon W. Byun, Violeta Coarfa,
The effect of pyro-convective fires on the global troposphere: comparison of TOMCAT modelled fields with observations from ICARTT Sarah Monks Outline:
Application of Models-3/CMAQ to Phoenix Airshed Sang-Mi Lee and Harindra J. S. Fernando Environmental Fluid Dynamics Program Arizona State University.
For more information about this poster please contact Gerard Devine, School of Earth and Environment, Environment, University of Leeds, Leeds, LS2 9JT.
New Techniques for Modeling Air Quality Impacts of DoD Activities Talat Odman and Ted Russell Environmental Engineering Department Georgia Institute of.
COST 723 WORKSHOP – SOFIA, BULGARIA MAY 2006 USE OF RADIOSONDE DATA FOR VALIDATION OF REGIONAL CLIMATE MODELLING SIMULATIONS OVER CYPRUS Panos Hadjinicolaou.
Impact of high resolution modeling on ozone predictions in the Cascadia region Ying Xie and Brian Lamb Laboratory for Atmospheric Research Department of.
Continued improvements of air quality forecasting through emission adjustments using surface and satellite data & Estimating fire emissions: satellite.
Optical Flow. Distribution of apparent velocities of movement of brightness pattern in an image.
Georgia Institute of Technology Adaptive Grid Modeling for Predicting the Air Quality Impacts of Biomass Burning Alper Unal, Talat Odman School of Civil.
U.S. EPA and WIST Rob Gilliam *NOAA/**U.S. EPA
1 Aika Yano, Yongtao Hu, M. Talat Odman, Armistead Russell Georgia Institute of Technology October 15, th annual CMAS conference.
Lagrangian particle models are three-dimensional models for the simulation of airborne pollutant dispersion, able to account for flow and turbulence space-time.
Seasonal Modeling of the Export of Pollutants from North America using the Multiscale Air Quality Simulation Platform (MAQSIP) Adel Hanna, 1 Rohit Mathur,
Types of Models Marti Blad Northern Arizona University College of Engineering & Technology.
Unscented Kalman Filter (UKF) CSCE 774 – Guest Lecture Dr. Gabriel Terejanu Fall 2015.
Aerospace Engineering N. C. State University Air Terminal Wake Vortex Simulation D. Scott McRae, Hassan A. Hassan N.C. State University 4 September 2003.
Georgia Institute of Technology SUPPORTING INTEX THROUGH INTEGRATED ANALYSIS OF SATELLITE AND SUB-ORBITAL MEASUREMENTS WITH GLOBAL AND REGIONAL 3-D MODELS:
Coupling a sub-grid scale plume model for biomass burns with adaptive grid CMAQ: part 2 Aika Yano Fernando Garcia-Menendez Yongtao Hu M. Talat Odman Gary.
Development of an Atmospheric Climate Model with Self-Adapting Grid and Physics Joyce E. Penner 1, Michael Herzog 2, Christiane Jablonowski 3, Bram van.
Pearl River Delta (PRD) The distribution of city clusters in China Analysis and numerical simulation on a server Fan Qi 1,Yu Wei 1, Luo Xuyu 1, (1. Department.
Georgia Institute of Technology Evaluation of the 2006 Air Quality Forecasting Operation in Georgia Talat Odman, Yongtao Hu, Ted Russell School of Civil.
Implementation of a direct sensitivity method into CMAQ Daniel S. Cohan, Yongtao Hu, Amir Hakami, M. Talat Odman, Armistead G. Russell Georgia Institute.
Implementation of an improved horizontal diffusion scheme into the Méso-NH Günther Zängl Laboratoire d’Aérologie / University of Munich 7 March 2005.
1 8 th Conference on Air Quality Modeling – AWMA AB3 Comments on Lagrangian and Eulerian Long Range Transport/Regional Models By Bob Paine, ENSR.
Albert Oliver, Raúl Arasa, Agustí Pérez-Foguet, Mª Ángeles González HARMO17 Budapest May 2016 Simulating large emitters using CMAQ and a local scale finite.
7. Air Quality Modeling Laboratory: individual processes Field: system observations Numerical Models: Enable description of complex, interacting, often.
Comparisons of CALPUFF and AERMOD for Vermont Applications Examining differing model performance for a 76 meter and 12 meter (stub) stack with emission.
Types of Models Marti Blad PhD PE
Volcanic Ash Detection and Prediction at the Met Office
Analysis of Vertical Fire Emissions Distribution in CMAQ
Using CMAQ to Interpolate Among CASTNET Measurements
Models of atmospheric chemistry
Fernando Garcia-Menendez
Synthesis of Motion from Simple Animations
Generation of Simulated GIFTS Datasets
Georgia Institute of Technology
Three-Dimensional Finite Element Modeling of Stack Pollutant Emissions
Local Scale Finite Element Modelling of Stack Pollutant Emissions
Development and Evaluation of a Hybrid Eulerian-Lagrangian Modeling Approach Beata Czader, Peter Percell, Daewon Byun, Yunsoo Choi University of Houston.
Presentation transcript:

TEMPLATE DESIGN © A high-order accurate and monotonic advection scheme is used as a local interpolator to redistribute the concentration onto the adapted grid: Three-dimensional adaptation may be fully unconstrained or vertically constrained, maintaining cell area constant throughout each stack of cells: Refinement is achieved by repositioning grid nodes in response to three- dimensional adaptation weight field: Key features: 1)Dynamic adaptation with simultaneous horizontal and vertical grid refinement 2)Total number of nodes and connectivity do not change during the simulation 3)A local coordinate transformation into a boundary-conforming curvilinear coordinate system is applied to use the air quality model’s original solution algorithms on adapting grid 4)Grid adaptation is achieved applying a 4-step iterative process Adaptive grid modeling can reduce artificial diffusion in CTMs and improve performance: Motivation Adaptive grids can be used to enhance the multiscale capabilities of grid-based air quality models. The technique is used to increase solution accuracy by dynamically refining the modeling grid in response to a model variable or parameter. Nearly all prior adaptive grid air quality modeling has been limited to horizontal refinement and vertical adaptation has not yet been explored in operational models. However, full three-dimensional grid adaptation would be valuable in simulations featuring concentrated plumes in the free troposphere, as well as plumes near inversions or the top of the boundary layer. Here a three-dimensional adaptive grid algorithm designed for chemical transport models is presented. The mesh-moving (r-refinement) method allows vertical and horizontal refinement to occur simultaneously yet retains a grid’s original structure, enhancing compatibility with existing air quality models. Advection tests are used to demonstrate the algorithm’s ability to better capture concentration gradients in atmospheric plumes. 1. Grid cell weighting Contact Information M. Talat Odman School of Civil and Environmental Engineering Georgia Institute of Technology 2D Adaptive Grid in CMAQ Adaptive grid dispersion test 1 Recommendations and challenges 3-D adaptation can benefit simulations of concentrated plumes in the free troposphere or near the top of the PBL where vertical grid resolution is typically coarse Vertically constrained adaptation may simplify implementation into existing models Global interpolation algorithms highly recommended for 3˗D adaptation Overall model resolution is still limited by resolution of meteorology and emissions inputs Atmospheric plume modeling with a three-dimensional refinement adaptive grid method M. Talat Odman, Yongtao Hu; School of Civil and Environmental Engineering, Georgia Institute of Technology Fernando Garcia-Menendez; Center for Global Change Science, Massachusetts Institute of Technology PM 2.5 (µg m -3 ) Adaptive Grid Fixed Grid (4km) 3-D Adaptive Grid Algorithm 2. Grid Movement Unconstrained adaptation: Vertically constrained adaptation: a) µg m -3 c) µg m -3 b) Adaptation Weight d) Adaptation Weight 3. Field Redistribution & 4. Grid Convergence z y x Computational Domain Physical Domain ζ η ξ Weights are assigned to each grid cell using a weight function based on model variables or parameters: Otherwise to Step 1 E Pollutant puff shown as a three-dimensional iso-surface bounded by PM 2.5 concentration equal to 10 µg m -3 crossing an intersection of X and Y grid planes. Grid lines and PM 2.5 concentrations (µg m -3 ) along the planes are also included. Side view of the adjusted weight fields (b and d) estimated from (a) blank and (c) single-cell-value concentration fields (µg m -3 ). Side view of grid response to a normalized weight field using unconstrained adaptation and vertically constrained three-dimensional adaptation Iterative grid adaptation continues until one of the grid convergence criteria is met: → either the grid nodes do not move significantly → or maximum number of iterations is reached Side view of three-dimensional iso-surfaces defined by PM 2.5 concentration equal to 10 μg m -3 in fixed and adaptive grid simulations 1, 5, and 10 hours after release of pollutant puff. Advection of an instantaneous pollutant puff under WRF-generated wind field: Adaptive grid dispersion test 2 Unconstrained adaptation: Vertically constrained adaptation: Y grid plane intersecting pollutant puff 5 hours after release simulated with unconstrained adaptation and vertically constrained three-dimensional adaptation. Maximum concentrations predicted by fixed and adaptive grid simulations are shown in adjacent plot. Three-dimensional refinement can improve simulations of continuous point sources by retaining higher concentrations along plume centerlines and reducing numerical diffusion: Adaptive Grid Fixed Grid Top view of PM 2.5 concentrations (µg m -3 ) simulated at 2000 m AGL under southeasterly wind field using fixed and adaptive grids Side view of PM 2.5 concentrations (µg m -3 ) simulated under uniform vertical wind field using fixed and adaptive grids