FMA Challenge 3: Difference between revisions

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*Understanding the Green and Ampt infiltration method and USDR soil types.<br>
 
DataDData for this model is provided viain ZIPa compressedvariety fileof availabledifferent [http://www.tuflow.com/Tuflow%20Tutorial%20Models.aspxGIS compatible onformats. Download the TUFLOWdataset Downloadsthat Page]matches underthe 'DemoGIS Models'.<br>software you are using:
*[https://www.tuflow.com/Download/TUFLOW/Demo_Models/FMA_Challenge_Model_3_QGIS.zip QGIS Data Download]
*[https://www.tuflow.com/Download/TUFLOW/Demo_Models/FMA_Challenge_Model_3_Mapinfo.zip MapInfo Data Download]
*[https://www.tuflow.com/Download/TUFLOW/Demo_Models/FMA_Challenge_Model_3_ArcGIS.zip ArcGIS Data Download]
 
=Relevant Tutorials=
Other tutorials that are relevant to this challenge that may help refresh your memory are as follows:<br>
*1D-2D Linking - <u>[[Tutorial Module02Tutorial_M03|Tutorial Module 23]]</u>
*1D Nested Channel - <u>[[Tutorial Module04Tutorial_M11|Tutorial Module 411]]</u>
*Running Events and Scenarios - <u>[[Tutorial Module10Tutorial_M08|Tutorial Module 108]]</u>
*Running Events - <u>[[Tutorial_M09|Tutorial Module 09]]</u>
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To check these Manning's 'n' assumptions, a sensitivity testing was completed on the in-bank roughness and is detailed further in the following sections.
 
==Boundary Conditions==
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[[File:FMA3_3.jpg|600px]]
 
==Levee Overtopping Assessment==
To assess the timing and location of where levee banks were overtopped, the TGC was setup with the evacuation route command:<br> <font color="blue"><tt>Read GIS Z Shape Route </tt></font> <font color="red"><tt>==</tt></font> shp\2d_zshr_T3_levees_001_L.shp | shp\2d_zsh_T3_levees_001_P.shp.<br>
Via review of the RC Map Output Data Type and the _RCP output point layer we can identify sections of the levee where a breach has occured (refer below).<br>
[[File:FMA3_6.jpg|600px]]
 
==Sensitivity Creek Manning's n Test (Scenario 100ft n0.1)==
As discussed in the Manning’s n table above, the main creek n value of 0.20 is considered very high, especially in the lower reaches of the study area. A sensitivity analysis was carried out by lowering all the Manning’s n values in the main channel (modeledmodelled as 1D cross-sections) to 0.10.
The image below shows the flood depths and extent for the two non-infiltration simulations at 100ft resolution (left with channel 'n' = 0.2, right with channel 'n' = 0.1). Some significant deviations in flood extent can be observed, particuallyparticularly sothsouth of the main channel. This can be largely attributed to the higher conveyance in the channel for the 'n'=0.1 case. <br>
[[File:FMA3_3.jpg|600px]][[File:FMA3_4.jpg|600px]]<br>
 
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[[File:FMA3_3.jpg|600px]][[File:FMA3_8.jpg|600px]]
 
==Challenges==
The soils GIS layers were difficult to work with. There is a lot of detail, but no clear way to correlate the different soils with Green-Ampt parameters (porosity, hydraulic conductivity, suction, etc).
 
=Conclusion=
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In this challenge, we explored typical non-urban stream of the California Central Valley, with scenarios of various infiltration and flood levees adopted. From this, we gained a better understanding of the influence of flood levees on surface water behaviour, understanding of the Green Ampt infiltration method and USDR soil types, and a better understanding of nested 1D/2D models.
 
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