Figure 2. Isopleths for dose rate (top) and fluence rate (bottom) as function of \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb}

Slides:



Advertisements
Similar presentations
Original Figures for "Molecular Classification of Cancer: Class Discovery and Class Prediction by Gene Expression Monitoring"
Advertisements

page 0 Prepared by Associate Prof. Dr. Mohamad Wijayanuddin Ali Chemical Engineering Department Universiti Teknologi Malaysia.
CHAPTER 5 Concentration Models: Diffusion Model.
Copyright © Cengage Learning. All rights reserved. 13 Linear Correlation and Regression Analysis.
AMBIENT AIR CONCENTRATION MODELING Types of Pollutant Sources Point Sources e.g., stacks or vents Area Sources e.g., landfills, ponds, storage piles Volume.
Dispersion of Air Pollutants The dispersion of air pollutants is primarily determined by atmospheric conditions. If conditions are superadiabatic a great.
Cases 1 through 10 above all depend on the specification of a value for the eddy diffusivity, K j. In general, K j changes with position, time, wind velocity,
Comparison of the AEOLUS3 Atmospheric Dispersion Computer Code with NRC Codes PAVAN and XOQDOQ 13th NUMUG Conference, October 2009, San Francisco, CA.
Consequence Analysis 2.2.
Copyright ©2015 Pearson Education, Inc. All rights reserved.
Recurrent uric acid stones by K.S. Kamel, S. Cheema-Dhadli, M.A. Shafiee, M.R. Davids, and M.L. Halperin QJM Volume 98(1):57-68 December 29, 2004 QJM vol.
Date of download: 6/3/2016 Copyright © 2016 SPIE. All rights reserved. Photon recycling processes in a single junction solar cell on a substrate illustrated.
Date of download: 6/27/2016 Copyright © ASME. All rights reserved. From: Optimal Control of a Formula One Car on a Three-Dimensional Track—Part 1: Track.
Date of download: 7/11/2016 Copyright © 2016 SPIE. All rights reserved. Scheme of the simulation arrangement. The red hour glass shape denotes the illumination.
Ventilation-perfusion Ratio
Date of download: 10/3/2017 Copyright © ASME. All rights reserved.
Date of download: 10/9/2017 Copyright © ASME. All rights reserved.
Date of download: 10/12/2017 Copyright © ASME. All rights reserved.
Figure 3. Count rates at the eight measurement locations at ZWILAG in the vicinity of a cask filled with spent fuel (left column) and a cask containing.
Fig. 2 Two-dimensional embedding result obtained using nMDS.
From: Variational Integrators for Structure-Preserving Filtering
Copyright © Cengage Learning. All rights reserved.
Date of download: 10/26/2017 Copyright © ASME. All rights reserved.
Figure 1. (a) A set-up used for the measurements showing the head phantom and the ion chamber located in the central hole. The cylindrical phantom has.
Figure 1. Schematic representation of the irradiation geometries to achieve different angles of incidence. S denotes the source; L is the distance from.
From: Accuracy of Wearable Sensors for Estimating Joint Reactions
Date of download: 12/22/2017 Copyright © ASME. All rights reserved.
Date of download: 12/27/2017 Copyright © ASME. All rights reserved.
Journal of Vision. 2017;17(8):6. doi: / Figure Legend:
Figure 2. Entrance dose at the detector for the clinical (light grey bars) and reference (dark bars) protocols. From: COMPARISON OF WIRELESS DETECTORS.
Figure 1. Example of phase shift angles among three different terns where one of them has been taken as a reference. From: Assessment of ELF magnetic fields.
Date of download: 3/4/2018 Copyright © ASME. All rights reserved.
Fig. 1. SA-induced the generation of \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath}
Heather L. Dean, Maureen A. Hagan, Bijan Pesaran  Neuron 
Analysis of mutational effects of parameters on the phenotype (i. e
Volume 20, Issue 5, Pages (May 1998)
Lial/Hungerford/Holcomb/Mullins: Mathematics with Applications 11e Finite Mathematics with Applications 11e Copyright ©2015 Pearson Education, Inc. All.
Chiu Shuen Hui, Henry R. Besch, Keshore R. Bidasee  Biophysical Journal 
Volume 6, Issue 5, Pages e13 (May 2018)
Heather L. Dean, Maureen A. Hagan, Bijan Pesaran  Neuron 
Spatiotemporal Response Properties of Optic-Flow Processing Neurons
Mismatch Receptive Fields in Mouse Visual Cortex
Scheme 1. Scheme of the quartz sample holder.
Figure 3. Values of the correction factor kmtx,j for the sixty energy channels j = 1,…,60. The values for ten iteration steps are shown. In addition, the.
Volume 20, Issue 5, Pages (May 1998)
Hierarchical empirical Bayesian inference on group effects using the function spm_dcm_peb. Hierarchical empirical Bayesian inference on group effects using.
Global mean temperatures are rising faster with time Warmest 12 years:
Γ-TEMPy: Simultaneous Fitting of Components in 3D-EM Maps of Their Assembly Using a Genetic Algorithm  Arun Prasad Pandurangan, Daven Vasishtan, Frank.
Spatial Coding of the Predicted Impact Location of a Looming Object
Cortical Mechanisms of Smooth Eye Movements Revealed by Dynamic Covariations of Neural and Behavioral Responses  David Schoppik, Katherine I. Nagel, Stephen.
Target Detection Is Enhanced by Polarization Vision in a Fiddler Crab
Christopher Deufel, Michelle D. Wang  Biophysical Journal 
Wind Velocity One of the effects of wind speed is to dilute continuously released pollutants at the point of emission. Whether a source is at the surface.
Modeling the Spatial Reach of the LFP
Spatial Coding of the Predicted Impact Location of a Looming Object
Origin and Function of Tuning Diversity in Macaque Visual Cortex
Volume 91, Issue 5, Pages (September 2016)
A Scalable Population Code for Time in the Striatum
Cian O’Donnell, Terrence J. Sejnowski  Neuron 
Samuel T. Hess, Watt W. Webb  Biophysical Journal 
Representation of Color Stimuli in Awake Macaque Primary Visual Cortex
Michael Schlierf, Felix Berkemeier, Matthias Rief  Biophysical Journal 
Dispersion Models Dispersion of pollutants in the atmosphere Models
Cell Growth and Size Homeostasis in Silico
Γ-TEMPy: Simultaneous Fitting of Components in 3D-EM Maps of Their Assembly Using a Genetic Algorithm  Arun Prasad Pandurangan, Daven Vasishtan, Frank.
Non-dimensional angular velocity of pitching rotation \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts}
Yongli Zhang, Junyi Jiao, Aleksander A. Rebane  Biophysical Journal 
Scattering and Interference in Epitaxial Graphene
Brand-specific incremental lifetime cancer risk subtotals: \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts}
George D. Dickinson, Ian Parker  Biophysical Journal 
Presentation transcript:

Figure 2. Isopleths for dose rate (top) and fluence rate (bottom) as function of \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\dot{Q}}/u\) \end{document} vs. h. The results are shown for A, C and F stability at a downwind distance of 500 m and at ground level. The full curves correspond to a detector placed below the plume centerline (y<sub>0</sub> = 0), whereas the dashed curves correspond to a detector placed at a crosswind distance of 300 m. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 1. Horizontal plume and receptor coordinates. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 7. Schematic drawing of the experimental setup Figure 7. Schematic drawing of the experimental setup. <sup>41</sup>Ar is emitted from the stack (S) and the primary photon fluence rate from <sup>41</sup>Ar decay is measured by detectors A through D. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 4. Simulated and Kalman filtered state variables, \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\hat{X}}_{t{\vert}t}\) \end{document} (left column). The solid black curves show the simulated variables, whereas the gray dashed and dot-dash lines show the Kalman filtered parameters using setup 1 (detectors 1–4) and setup 2 (detectors 3–6), respectively. The associated standard deviations, \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\surd}\left({\Sigma}_{t{\vert}t}^{xx}\right)_{ii}\) \end{document}, are shown in the right column. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 5. Simulated dose rate and wind direction measurements for setup 1 (left column) and setup 2 (right column). The solid curves show the simulated data whereas the dashed lines show the filter-predicted values \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\hat{Y}}_{t{\vert}t{-}1}\) \end{document}. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 3. The simulation setup Figure 3. The simulation setup. ‘S’ indicates the stack position while ‘1–6’ denote the six detectors. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 6. Parameter correlations calculated from the a posteriori error covariance matrix, \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\Sigma}_{t{\vert}t}^{xx}\) \end{document}. The dashed and dot-dashed curves show the results for setup 1 and setup 2, respectively. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 8. The solid curves show the fluence rate measurements obtained by the gamma detectors A–D and the wind direction measurements, whereas the dashed curves show the Kalman filter predictions, \batchmode \documentclass[fleqn,10pt,legalpaper]{article} \usepackage{amssymb} \usepackage{amsfonts} \usepackage{amsmath} \pagestyle{empty} \begin{document} \({\hat{Y}}_{t{\vert}t{-}1}\) \end{document}. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved

Figure 9. The Kalman filtered state variables (left) and associated standard deviations (right). The solid curves show measured values, whereas the dashed curves are the Kalman filter estimates. The Lidar estimates of h at the downwind distance of the detectors (∼200 m) are obtained by linear interpolation between the release height (stack height) and the Lidar measured plume height at ∼400 m from the release point. From: Kalman filtration of radiation monitoring data from atmospheric dispersion of radioactive materials Radiat Prot Dosimetry. 2004;111(3):257-269. doi:10.1093/rpd/nch339 Radiat Prot Dosimetry | Radiation Protection Dosimetry Vol. 111, No. 3 © Oxford University Press 2004; all rights reserved