1 | \section{Introduction} |
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2 | Tsunami is a potential hazard to coastal communities all over the |
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3 | world. A number of recent large events have increased community and |
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4 | scientific awareness of the need for effective detection, forecasting, |
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5 | and emergency preparedness. Probabilistic, geophysical and hydrodynamic |
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6 | models are required to predict the location and |
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7 | likelihood of an event, the initial sea floor deformation and |
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8 | subsequent propagation and inundation of the tsunami. Engineering, economic and social vulnerability models can then be used to estimate the |
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9 | impact of the event as well as the effectiveness of hazard mitigation |
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10 | procedures. In this paper, we focus on modelling of |
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11 | the physical processes only. |
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12 | |
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13 | Various approaches are currently used to assess the potential tsunami |
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14 | inundation of coastal communities. |
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15 | These methods differ in both the formulation used to |
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16 | describe the evolution of the tsunami and the numerical methods used |
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17 | to solve the governing equations. The structure of these models ranges |
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18 | from data-driven neural networks~\cite{romano09} to |
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19 | non-linear three-dimensional mechanical models~\cite{zhang08}. |
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20 | These models are typically used to predict quantities such as arrival |
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21 | times, wave speeds and heights, and inundation extents |
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22 | which are used to develop efficient hazard mitigation plans. Physics based |
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23 | models combine observed seismic, geodetic and sometimes tsunami data to |
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24 | provide estimates of initial sea floor and ocean surface |
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25 | deformation. Whilst the shallow water wave equations~\cite{george06}, |
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26 | linearised shallow water wave equations~\cite{liu09}, |
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27 | and Boussinesq-type equations~\cite{weiss06} are frequently used to simulate |
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28 | tsunami propagation and inundation. |
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29 | |
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30 | Inaccuracies in model prediction can result in inappropriate |
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31 | evacuation plans and town zoning, which may result in loss of life and |
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32 | large financial losses. Consequently tsunami models must undergo |
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33 | sufficient end-to-end testing to increase scientific and community |
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34 | confidence in the model predictions. |
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35 | |
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36 | Complete confidence in a model of a physical system cannot be |
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37 | established. One can only hope to state under what conditions and to |
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38 | what extent the |
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39 | model hypothesis holds true. Specifically the utility of a model can |
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40 | be assessed through a process of verification and |
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41 | validation. Verification assesses the accuracy of the numerical method |
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42 | used to solve the governing equations and validation is used to |
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43 | investigate whether the model adequately represents the physical |
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44 | system~\cite{bates01}. Together these processes can be used to |
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45 | establish the likelihood that a model represents a legitimate |
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46 | hypothesis. |
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47 | |
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48 | The sources of data used to validate and verify a model can be |
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49 | separated into three main categories: analytical solutions, scale |
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50 | experiments and field measurements. Analytical solutions, of the |
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51 | governing equations of a model, if available, provide the best means |
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52 | of verifying any numerical model. However, analytical solutions are |
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53 | frequently limited to a small set of idealised examples that do not |
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54 | completely capture the more complex behaviour of `real' events. Scale |
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55 | experiments, typically in the form of wave-tank experiments, provide a |
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56 | much more realistic source of data that better captures the complex |
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57 | dynamics of flows such as those generated by a tsunami, whilst allowing |
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58 | control of the event and much easier and accurate measurement of the |
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59 | tsunami properties. Comparison of numerical predictions with field |
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60 | data provides the most stringent test. The use of field data increases |
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61 | the generality and significance of conclusions made regarding model |
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62 | utility~\cite{bates01}. |
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63 | |
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64 | Currently, the extent of tsunami-related field data is limited. The |
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65 | cost of tsunami monitoring programs, bathymetry and topography surveys |
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66 | prohibits the collection of data in many of the regions in which |
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67 | tsunamis pose greatest threat. The resulting lack of data has limited |
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68 | the number of field data sets available to validate tsunami |
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69 | models. |
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70 | |
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71 | Synolakis et al~\cite{synolakis08} have developed a set of |
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72 | standards, criteria and procedures for evaluating numerical models of |
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73 | tsunami. They propose a number of analytical solutions to help identify the |
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74 | validity of a model, and five scale comparisons (wave-tank benchmarks) |
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75 | and two field events to assess model veracity. |
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76 | |
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77 | The first field data benchmark introduced in \cite{synolakis08} compares model |
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78 | results against observed data from the Hokkaido-Nansei-Oki tsunami |
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79 | that occurred around Okushiri Island, Japan on the 12 July |
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80 | 1993. This tsunami provides an example of extreme run-up generated from |
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81 | reflections and constructive interference resulting from local |
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82 | topography and bathymetry. The benchmark consists of two tide gauge |
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83 | records and numerous spatially-distributed point sites at which |
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84 | modelled maximum run-up elevations can be compared. The second |
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85 | benchmark is based upon the Rat Islands tsunami that occurred off the |
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86 | coast of Alaska on the 17 November 2003. The Rat Island tsunami |
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87 | provides a good test for real-time forecasting models since the tsunami |
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88 | was recorded at three tsunameters. The test requires matching the |
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89 | tsunami propagation model output with the tsunameter recordings to constrain |
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90 | the tsunami source model, and then using it to reproduce the tide gauge |
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91 | record at Hilo, Hawaii. |
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92 | |
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93 | In this paper we develop a field data benchmark to be used in |
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94 | conjunction with the other tests proposed by Synolakis et |
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95 | al~\cite{synolakis08} to validate and verify tsunami models. |
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96 | The benchmark proposed here allows evaluation of |
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97 | model structure during all three distinct stages tsunami evolution. |
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98 | It consists of geodetic measurements of the |
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99 | Sumatra--Andaman earthquake that are used to validate the description |
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100 | of the tsunami source, altimetry data from the \textsc{jason} satellite to test |
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101 | open ocean propagation, eye-witness accounts to assess near shore |
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102 | propagation, and a detailed inundation survey of Patong city, Thailand |
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103 | to compare model and observed inundation. A description of the data |
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104 | required to construct the benchmark is given in |
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105 | Section~\ref{sec:data}. |
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106 | |
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107 | Previous model field evaluations~\cite{watts05,ioualalen07} and |
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108 | benchmarks~\cite{synolakis08} have focused on reproducing inundation at |
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109 | point sites, which are often sparsely distributed. The stakeholders in |
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110 | any tsunami study, such as emergency planners are generally more interested |
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111 | in more detailed localised studies of tsunami impacts on populated areas. |
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112 | Informed and defensible decisions must be based upon detailed simulations |
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113 | that predict local inundation extents. Ideally validation studies should be |
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114 | tailored accordingly. |
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115 | |
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116 | Unlike the existing field benchmarks the proposed test does facilitate |
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117 | localised and highly detailed spatially distributed assessment of |
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118 | modelled inundation. To the authors knowledge it is also the first benchmark to |
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119 | assess model inundation under influenced by numerous human structures. |
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120 | Eye-witness videos also allow the qualitative assessment of onshore flow |
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121 | patterns. |
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122 | |
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123 | An associated aim of this paper is to illustrate the use of this new |
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124 | benchmark to validate the three step modelling methodology employed by |
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125 | Geoscience Australia to model tsunami inundation. A description of the model |
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126 | components is provided in Section~\ref{sec:models} and the validation |
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127 | results are given in Section~\ref{sec:results}. |
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128 | |
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129 | The numerical models used to simulate tsunami impact |
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130 | are computationally intensive and high resolution models of the entire |
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131 | evolution process will often take a number of days to |
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132 | run. Consequently, the uncertainty in model predictions is difficult to |
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133 | quantify as it would require a very large number of runs. |
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134 | However, model uncertainty should not be ignored. Section |
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135 | ~\ref{sec:sensitivity} provides a simple analysis that can |
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136 | be used to investigate the sensitivity of model predictions to a number |
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137 | of model parameters. |
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