model was used to dem<strong>on</strong>strate that both <strong>the</strong> channelnetwork (including <strong>the</strong> c<strong>on</strong>nectivity provided by floodplainchannels) and floodplain storage are necessary to simulate<strong>the</strong> correct wave propagati<strong>on</strong>. The calibrati<strong>on</strong> <strong>of</strong> <strong>the</strong> sub-gridchannel model from <strong>the</strong> available remotely sensed data setsand prospects for assimilating data with <strong>the</strong> model <strong>on</strong> ungaugedrivers were also evaluated.Neale, Christopher M.Water balance <strong>of</strong> Large Irrigati<strong>on</strong> Systems using<strong>Remote</strong>ly Sensed ET EstimatesNeale, Christopher M. 1 ; Taghvaeian, Saleh 1 ; Geli, Hatim 11. Civil and Envir<strong>on</strong>mental Eng., Utah State University,Logan, UT, USADemand for water for urban/municipal uses c<strong>on</strong>tinuesto rise in <strong>the</strong> Western US with <strong>the</strong> growing populati<strong>on</strong>. Mostfresh water is tied up in irrigated agriculture thusunderstanding <strong>the</strong> pathways <strong>of</strong> irrigati<strong>on</strong> water and <strong>the</strong>c<strong>on</strong>sumptive use <strong>of</strong> water within large irrigati<strong>on</strong> systemsbecomes <strong>of</strong> vital importance for improved rivermanagement, policy decisi<strong>on</strong>s and water transfers. In thispaper we examine <strong>the</strong> use <strong>of</strong> different remote sensingmethods for estimating evapotranspirati<strong>on</strong> (ET), namely <strong>the</strong>energy balance method and <strong>the</strong> reflectance-based cropcoefficient method for estimating seas<strong>on</strong>al ET at <strong>the</strong> PaloVerde Irrigati<strong>on</strong> District (PVID) in sou<strong>the</strong>rn, CA. Two energybalance methods are tested, namely <strong>the</strong> Two-source model by(Norman et al., 1995) and <strong>the</strong> Surface Energy Balance forLand (SEBAL) method (Bastiaansen et al., 1998). Thereflectance-based crop coefficient method as originallydescribed by Neale et al, 1989, Bausch and Neale, 1987 is alsoapplied. The PVID system diverts water from <strong>the</strong> ColoradoRiver through an extensive network <strong>of</strong> canals. Water flowmeasurements are c<strong>on</strong>ducted in <strong>the</strong> inflow to <strong>the</strong> system aswell as <strong>the</strong> main outflow drain and all spill locati<strong>on</strong>s at <strong>the</strong>end <strong>of</strong> lateral canals, allowing a complete water balance to beestimated for this 53000 ha irrigati<strong>on</strong> system. An extensivenetwork <strong>of</strong> groundwater wells allowed for <strong>the</strong> m<strong>on</strong>itoring <strong>of</strong>deep percolati<strong>on</strong> and drainage. We close <strong>the</strong> yearly waterbalance using estimates <strong>of</strong> ET from <strong>the</strong> different remotesensing based models. Daily ET values from <strong>the</strong> differentmodels are compared to Bowen ratio and eddy covariance ETmeasurements from towers placed in alfalfa and cott<strong>on</strong>respectively. The PVID is located in <strong>the</strong> overlap z<strong>on</strong>e betweentwo Landsat TM paths, which resulted in 21 usable imagesduring 2008 (Taghvaeian, 2011) and allowed for a detailedexaminati<strong>on</strong> <strong>of</strong> seas<strong>on</strong>al ET by <strong>the</strong> different models.Nearing, GreyEstimating Thermal Inertia with a MaximumEntropy Producti<strong>on</strong> Boundary C<strong>on</strong>diti<strong>on</strong>Nearing, Grey 1 ; Moran, Susan 2 ; Scott, Russell 21. Hydrology and Water Resources, University <strong>of</strong> Ariz<strong>on</strong>a,Tucs<strong>on</strong>, AZ, USA2. Southwest Watershed Research Center, USDA-ARS,Tucs<strong>on</strong>, AZ, USAThermal inertia, P [Jm-2s-1/2K-1], is a physical property<strong>the</strong> land surface which determines resistance to temperaturechange under seas<strong>on</strong>al or diurnal heating. It is a functi<strong>on</strong> <strong>of</strong>volumetric heat capacity, c [Jm-3K-1], and <strong>the</strong>rmalc<strong>on</strong>ductivity, k [Wm-1K-1] <strong>of</strong> <strong>the</strong> soil near <strong>the</strong> surface:P=ck. Thermal inertia <strong>of</strong> soil varies with moisture c<strong>on</strong>tentdue <strong>the</strong> difference between <strong>the</strong>rmal properties <strong>of</strong> water andair, and a number <strong>of</strong> studies have dem<strong>on</strong>strated that it isfeasible to estimate soil moisture given <strong>the</strong>rmal inertia (e.g.Lu et al, 2009). One comm<strong>on</strong> approach to estimating<strong>the</strong>rmal inertia using measurements <strong>of</strong> surface temperatureis to model <strong>the</strong> Earth’s surface as a 1-dimensi<strong>on</strong>alhomogeneous diffusive half-space and derive surfacetemperature as a functi<strong>on</strong> <strong>of</strong> <strong>the</strong> ground heat flux (G)boundary c<strong>on</strong>diti<strong>on</strong> and <strong>the</strong>rmal inertia; a daily value <strong>of</strong> P isestimated by matching measured and modeled diurnalsurface temperature fluctuati<strong>on</strong>s. The difficulty in applyingthis technique is in measuring G, and a number <strong>of</strong>approaches have been suggested (e.g. Xue and Cracknell,1995). We dem<strong>on</strong>strate that <strong>the</strong> new maximum entropyproducti<strong>on</strong> (MEP) method for partiti<strong>on</strong>ing net radiati<strong>on</strong>into surface energy fluxes (Wang and Bras, 2011) provides asuperior boundary c<strong>on</strong>diti<strong>on</strong> for estimating P. Adding <strong>the</strong>diffusi<strong>on</strong> representati<strong>on</strong> <strong>of</strong> heat transfer in <strong>the</strong> soil reduces<strong>the</strong> number <strong>of</strong> free parameters in <strong>the</strong> MEP model from twoto <strong>on</strong>e, and we provide a sensitivity analysis which suggests,for <strong>the</strong> purpose <strong>of</strong> estimating P, that it is preferable toparameterize <strong>the</strong> MEP model by <strong>the</strong> ratio <strong>of</strong> <strong>the</strong>rmal inertia<strong>of</strong> <strong>the</strong> soil to <strong>the</strong> effective <strong>the</strong>rmal inertia <strong>of</strong> c<strong>on</strong>vective heattransfer to <strong>the</strong> atmosphere. Estimates <strong>of</strong> <strong>the</strong>rmal inertia attwo semiarid, n<strong>on</strong>-vegetated locati<strong>on</strong>s in <strong>the</strong> Walnut GulchExperimental Watershed in sou<strong>the</strong>ast AZ, USA are madeusing time series <strong>of</strong> ground heat flux measurements and<strong>the</strong>se are compared to estimates <strong>of</strong> <strong>the</strong>rmal inertia madeusing <strong>the</strong> boundary c<strong>on</strong>diti<strong>on</strong> suggested by Xue andCracknell (1995) and those made with <strong>the</strong> MEP ground heatflux boundary c<strong>on</strong>diti<strong>on</strong>. Nash-Sutcliffe efficiencycoefficients for predicti<strong>on</strong>s made using <strong>the</strong> MEP boundaryc<strong>on</strong>diti<strong>on</strong> are NSE = 0.44 and NSE = 0.59 at <strong>the</strong> two sitedcompared to NSE = -12.31 and NSE = -6.81 using <strong>the</strong> Xueand Cracknell boundary c<strong>on</strong>diti<strong>on</strong>. Thermal inertiameasurements made using <strong>the</strong> MEP boundary c<strong>on</strong>diti<strong>on</strong> areextrapolated to daily near-surface soil moisture estimatesusing <strong>the</strong> model developed by Lu et al (2009). In very dryc<strong>on</strong>diti<strong>on</strong>s, <strong>the</strong>rmal inertia is less sensitive to changes in soilmoisture than in moderate-to-wet c<strong>on</strong>diti<strong>on</strong>s. Overall wefind <strong>the</strong> correlati<strong>on</strong> between measured and modeled soilmoisture at <strong>the</strong>se semiarid sites to be approximately 0.5.Lu, S., Ju, Z.Q., Ren, T.S., & Hort<strong>on</strong>, R. (2009). A general110
approach to estimate soil water c<strong>on</strong>tent from <strong>the</strong>rmalinertia. Agricultural and Forest Meteorology, 149, 1693-1698Wang, J.F., & Bras, R.L. (2011). A model <strong>of</strong>evapotranspirati<strong>on</strong> based <strong>on</strong> <strong>the</strong> <strong>the</strong>ory <strong>of</strong> maximumentropy producti<strong>on</strong>. Water Resources Research, 47 Xue, Y., &Cracknell, A.P. (1995). Adavanced <strong>the</strong>rmal inertia modeling.Internati<strong>on</strong>al Journal <strong>of</strong> <strong>Remote</strong> <strong>Sensing</strong>, 16, 431-446Négrel, JeanRiver surface roughness sensitivity to windc<strong>on</strong>diti<strong>on</strong>s : in situ measurement technique,processing method and resultsNégrel, Jean 1 ; Kosuth, Pascal 1 ; Caulliez, Guillemette 2 ;Strauss, Olivier 3 ; Borderies, Pierre 4 ; Lalaurie, Jean-Claude 5 ;Fjort<strong>of</strong>t, Roger 51. UMR TETIS, IRSTEA, M<strong>on</strong>tpellier, France2. IRPHE, CNRS, Marseille, France3. LIRMM, Université M<strong>on</strong>tpellier 2, M<strong>on</strong>tpellier, France4. DEMR, ONERA, Toulouse, France5. DCT/SI/AR, CNES, Toulouse, FranceWater surface roughness str<strong>on</strong>gly impacts microwavebackscattering process over rivers. Therefore, developpingradar interferometry techniques over c<strong>on</strong>tinental waters todetermine river slope (cross-track interferometry) or surfacevelocity (al<strong>on</strong>g-track interferometry) requires a detailedcharacterizati<strong>on</strong> <strong>of</strong> water surface roughness, its relati<strong>on</strong> withriver flow and wind c<strong>on</strong>diti<strong>on</strong>s, its influence <strong>on</strong> backscattercoefficient. In situ measurement <strong>of</strong> river surface roughness isa complex task as surface topography is rapidly changingand sensitive to obstacles or c<strong>on</strong>tact measurements.Laboratory measurements, although highly informative, fallshort to represent <strong>the</strong> diversity <strong>of</strong> river flow and windc<strong>on</strong>diti<strong>on</strong>s. In <strong>the</strong> framework <strong>of</strong> <strong>the</strong> SWOT missi<strong>on</strong>preparatory phase, a method was developped for fieldmeasurement <strong>of</strong> river surface roughness. It was tested andvalidated in laboratory c<strong>on</strong>diti<strong>on</strong>s, and implemented innatural c<strong>on</strong>diti<strong>on</strong>s <strong>on</strong> <strong>the</strong> Rhône river, under various windintensities. The method is based <strong>on</strong> <strong>the</strong> acquisiti<strong>on</strong> <strong>of</strong> waterpressure time series by a network <strong>of</strong> immersed pressuresensors, with synchr<strong>on</strong>ized 10 Hz sampling and 0,1 mbaraccuracy (1mm water elevati<strong>on</strong>). A preliminary low frequencyfiltering is applied to each sensor pressure time series toremove water level trends. Mean depth h, frequencyspectrum, dominant frequency f and standard deviati<strong>on</strong> <strong>of</strong>water pressure Pare determined per time interval (180s). Amultisensor analysis is realised to determine directi<strong>on</strong>al wavecelerity c and directi<strong>on</strong>al correlati<strong>on</strong> length L corr. Finallystandard deviati<strong>on</strong> <strong>of</strong> surface water level Zis determined foreach sensor by applying a correcti<strong>on</strong> factor, taking intoaccount <strong>the</strong> signal damping with depth. Z=e 2.pi.h.f/c . P(h)Laboratory tests validated <strong>the</strong> measurement technique,provided that <strong>the</strong> correcti<strong>on</strong> factor does not exceed 10 (i.e.<strong>the</strong> immersed sensor records more than 10% <strong>of</strong> <strong>the</strong> surfacesignal) which is achievable by limiting <strong>the</strong> sensor depth.Field measurements were realised during a campaign <strong>on</strong> <strong>the</strong>Rhône river (may 2011). The sensor network was located10m from <strong>the</strong> river bank and 0,15m under <strong>the</strong> surface water.It recorded during 7 hours at 10 Hz. Wind measured at 2mheight had <strong>the</strong> same directi<strong>on</strong> as river flow (southward),with intensity changing progressively from 8m/s to 0m/s.Surface roughness was characterized, per 3 minute timeintervals, by Frequency spectrum, dominant frequency,standard deviati<strong>on</strong> <strong>of</strong> surface water level Z, directi<strong>on</strong>al wavecelerity c and directi<strong>on</strong>al correlati<strong>on</strong> distance L corr. Itssensitivity to wind c<strong>on</strong>diti<strong>on</strong>s was analysed and modelled.The method is currently being adapted <strong>on</strong> a floating supportfor intensive river surface roughness measurement.Njoku, Eni G.Soil Moisture Active Passive (SMAP) Missi<strong>on</strong>Science and Data Product DevelopmentNjoku, Eni G. 1 ; Entekhabi, Dara 2 ; O’Neill, Peggy E. 3 ;Jacks<strong>on</strong>, Thomas J. 41. Jet Propulsi<strong>on</strong> Laboratory, California Institute <strong>of</strong>Technology, Pasadena, CA, USA2. Massachusetts Institute <strong>of</strong> Technology, Cambridge, MA,USA3. NASA Goddard Space Flight Center, Greenbelt, MD, USA4. USDA ARS Hydrology and <strong>Remote</strong> <strong>Sensing</strong> Laboratory,Beltsville, MD, USAThe Soil Moisture Active Passive (SMAP) missi<strong>on</strong>,planned for launch in late 2014, has <strong>the</strong> objective <strong>of</strong>frequent, global mapping <strong>of</strong> near-surface soil moisture andits freeze/thaw state. The SMAP measurement systemutilizes an L-band radar and radiometer sharing a rotating 6-meter mesh reflector antenna. The instruments will operate<strong>on</strong> a spacecraft in a 685-km polar orbit with 6 am/6 pmnodal crossings, viewing <strong>the</strong> surface at a c<strong>on</strong>stant 40-degreeincidence angle with a 1000-km swath width, providing 3-day global coverage. Data from <strong>the</strong> instruments will yieldglobal maps <strong>of</strong> soil moisture and freeze/thaw state at 10 kmand 3 km resoluti<strong>on</strong>s, respectively, every two to three days.The 10-km soil moisture product will be generated using acombined radar and radiometer retrieval algorithm. SMAPwill also provide a radiometer-<strong>on</strong>ly soil moisture product at40-km spatial resoluti<strong>on</strong> and a radar-<strong>on</strong>ly soil moistureproduct at 3-km resoluti<strong>on</strong>. The relative accuracies <strong>of</strong> <strong>the</strong>seproducts will vary regi<strong>on</strong>ally and will depend <strong>on</strong> surfacecharacteristics such as vegetati<strong>on</strong> water c<strong>on</strong>tent, vegetati<strong>on</strong>type, surface roughness, and landscape heterogeneity. TheSMAP soil moisture and freeze/thaw measurements willenable significantly improved estimates <strong>of</strong> <strong>the</strong> fluxes <strong>of</strong>water, energy and carb<strong>on</strong> between <strong>the</strong> land and atmosphere.Soil moisture and freeze/thaw c<strong>on</strong>trols <strong>of</strong> <strong>the</strong>se fluxes arekey factors in <strong>the</strong> performance <strong>of</strong> models used for wea<strong>the</strong>rand climate predicti<strong>on</strong>s and for quantifying <strong>the</strong> global111
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Alfieri, Joseph G.The Factors Influ
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Courault, DominiqueAssessment of mo
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storage change solutions in the for
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