

Available online at www.sciencedirect.comJournal of Integrative Agriculture2013, 12(8): 1371-1388心ScienceDirectAugust 2013RESEARCH ARTICLECalifornia Simulation of Evapotranspiration of Applied Water and AgriculturalEnergy Use in CaliforniaMorteza N Orang', Richard L Snyder2, Shu Geng23, Quinn J Hart, Sara Sarreshteh2, Matthias Falk2, DylanBeaudette, Scott HayesI and Simon Eching'2 Department of Land, Air and Water Resources, University of California, Davis, CA 95616, USA3 School of Environment and Energy, Shenzhen Graduate School, Peking University, Shenzhen 518055, P.R.ChinaAbstractThe Califormia Simulation of Evapotranspiration of Applied Water (CaI-SIMETAW) model is a new tool developed by theCalifornia Department of Water Resources and the University of California, Davis to perform daily soil water balance anddetermine crop evapotranspiration (ET), evapotranspiration of applied water (ETgw), and applied water (AW) for use inCalifornia water resources planning. ETw is a seasonal estimate of the water needed to irrigate a crop assuming 100%irrigation efficiency. The model accounts for soils, crop cofficients, rooting depths, seepage, etc. that influence crop waterbalance. It provides spatial soil and climate information and it uses historical crop and land-use category information toprovide seasonal water balance estimates by combinations of detailed analysis unit and county (DAU/County) over California.The result is a large data base of ET。and ET that will be used to update information in the new California Water Plan (CWP).The application uses the daily climate data, i.e., maximum (T) and minimum (T) temperature and precipitation (Pp), whichwere derived from monthly USDA-NRCS PRISM data (PRISM Group 2011) and daily US National Climate Data Center(NCDC) climate station data to cover California on a 4 kmx4 km change grid spacing. The application uses daily weather datato determine reference evapotranspiration (ET.), using the Hargreaves-Samani (HS) equation (Hargreaves and Samani 1982,1985). Because the HS equation is based on temperature only, ET。from the HS equation were compared with CIMIS ET。atthe same locations using available CIMIS data to determine correction factors to estimate CIMIS ET。from the HS ET。toaccount for spatial climate differences. Cal SIMETAW also employs near real-time reference evapotranspiration (ET.)information from Spatial CIMIS, which is a model that combines weather station data and remote sensing to provide a grid ofET. information. A second database containing the available soil water holding capacity and soil depth information for all ofCalifornia was also developed from the USDA-NRCS SSURGO database. The Cal-SIMETAW program also has the ability togenerate daily weather data from monthly mean values for use in studying climate change scenarios and their possibleimpacts on water demand in the state. The key objective of this project is to improve the accuracy of water use estimates forthe California Water Plan (CWP), which provides a comprehensive report on water supply, demand, and management inCalifornia. In this paper, we will discuss the model and how it determines ETw for use in water resources planning.Key words: soil water balance, crop water requirements, weather generator, water resource planning, crop coffcient, energy usetion of Evapotranspiration of Applied Water or Cal-INTRODUCTIONSIMETAW was specifically designed to provide the bestpossible information on agricultural water demand forThe daily soil water balance model California Simula-use in the California Water Plan, updated every five中国煤化工Received 17 October, 2012 Acepted 10 January, 2013YHCNMHGCorrespondence Morteza N Orang. Tel: +1-916-6537707, E-mail: morang @ water.ca gov⑥2013,CAAS. All nghts rseved. PulisedbylEseviertd.1372Morteza N Orang et al. .years to present the status and trends of California'swater requirement. It differs from irrigation efficiency,water- dependent natural resources; water supplies; andwhich includes the crop water requirements, water usedagricultural, urban, and environmental water demandsfor frost protection, and leaching requirements, i.e.,for a range of plausible future scenarios. Californiabeneficial uses, divided by AW over a cropping season.agriculture is a multibillion dollar industry, number oneA major goal of this project was to improve infor-producer in the nation, and largest consumer of water.mation on current and future water demand. Cal-The agricultural water demand is high and increasing SIMETAW was developed for water demand planningbecause water supplies are limited and competition forand it can help to plan for the effects of climate changethose supplies is growing. The main factors that areas well as for current climate conditions. Improve-causing increases in agricultural water demand are thements to the input information and data processing inpopulation growth and demand for food and fiber. At Cal-SIMETAW greatly enhances our ability to rapidlythe same time, the demand for urban and environmen-and accurately determine ETaw for 20 crop categoriestal water uses is increasing. The California Depart- and 4 land-use categories by each DAU/County withinment of Water Resources (DWR) and the University ofCalifornia. All of the ET w calculations are done on aCaliformia, Davis (UC Davis) are keenly aware of thedaily basis, so the estimation of effective seepage ofneed for good planning, and Cal-SIMETAW model wasgroundwater, effective rainfall and, hence, ETw isdeveloped to address the planning needs. The Cal-greatly improved over earlier methods. In addition, theSIMETAW computer application program was writtenuse of the widely adopted Penman-Monteith equationusing Microsoft C# for calculations and Oracle Spatialfor reference evapotranspiration (ET) and improved11g for data storage, as a tool to help DWR obtain ac-methodology to apply crop coefficients for estimatingcurate estimates of crop evapotranspiration (ET),crop evapotranspiration (ET) is used to improve ETWevapotranspiration of applied water (ET) for agricul-accuracy for climate change and long-range water re-tural crops, and urban landscapes, which account for source planning.most evapotranspiration losses and water contributionsCal-SIMETAW uses batch processing to read (1) thefrom ground water seepage, precipitation, and irrigation.climate data, (2) the surface/crop coefficient values,Crop evapotranspiration is computed as the product(3) growth dates to estimate annual curves, (4) soilof reference evapotranspiration (ET) and a crop coef- information, (5) crop and irrigation information, andficient (K) value, i.e., ET =ET ,xK, and ET , which is(6) surface area of each crop and land-use category onequal to the seasonal evapotranspiration minus watereach of the 482 DAU/Counties. Then, the programsupplied by stored soil moisture, effective rainfall, andcomputes daily ET, K. factors, ET。, daily water balance,seepage from canals. Cal-SIMETAW accounts for effective rainfall, ETw, etc. for every surface withincontributions from rainfall and for ground water seep-each of the 482 DAU/Counties over the period of record.age from the rivers and canals when spatial informa-The water balance model is similar to that used in thetion on the depth to water table is available on theSimulation of ET of Applied Water (SIMETAW) applica-same 4 kmx4 km grid spacing used to characterizetion program, which was also developed as a coopera-soils within California.tive effort between the UC Davis and the DWR (SnyderCal-SIMETAW has the capability to estimate appliedet al. 2012). The main difference between the originalwater (AW) by crop and land-use category for eachSIMETAW model and Cal-SIMETAW is that SIMETAWdetailed analysis unit and county (DAU/County) com-uses historical or generated climate data to determine abination in the state. Applied water is estimated as thedaily water balance for individual cropped fields within aET divided by the mean seasonal irrigation systemwatershed region having one set of ET。estimates,application efficiency. Thus, the AW supplies estimateswhereas Cal-SIMETAW uses historical or generated cli-of the diversions needed by DWR to plan its futuremate data and batch fles of soil and climate data to com-water demand for irrigated agriculture. Seasonal sys-pute daily water balance for 20 crop categories, 4 land-tem application efficiency is an estimate of the fractionuse categories中国煤化IDAUCountyof AW irigation water is used to contribute to the crops regions that exhYHCNMHGdemandand⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1373rainfall. Cal-SIMETAW was designed to reduce the timethe USDA-NRCS SSURGO database (SSURGO 2011).needed for data input and to improve the water use/de-The developed data base covers all of California on themand estimates needed for the California Water Plan.same 4 kmx4 km grid as was used in the SSURGOThe simulation component of Cal-SIMETAW is use-database.ful for studying the effect of climate (e.g., temperature,Using mean soil characteristics and climate and ET。humidity, CO2 concentration, and rainfall) change on crop information from the 4 kmx4 km grid, Cal- SIMETAWevapotranspiration (ET) and evapotranspiration of ap- estimates the mean soil characteristics and ET。infor-plied water (ET、). One of main features of Cal-mation by DAU/County. The PRISM climate data baseSIMETAW is that it can simulate daily weather data from(PRISM Group 201 1), the Hargreaves Samani equation,monthly climate data, and the simulated data are used toand a calibration factor to convert ETys to ET。are usedestimate reference ET。Because of this feature, Cal-to estimate reference evapotranspiration (ET). CropSIMETAW allows the examination of the impact of mul-evapotranspiration is estimated using the single CrOPtiple management scenarios on agricultural water demandcoefficient approach (Doorenbos and Pruitt 1977; Allenusing GCM scenarios and regional downsizing models.et al. 1998). Up to 20 crop and 4 land-use categoriesUsing different climate change scenarios ftom GCMare used to determine weighted crop coefficients tomodels and a downsizing model to determine means ofestimate crop evapotranspiration (ET) using the singlemonthly climate data for 2030 and 2050, Cal-SIMETAWcrop coefficient approach (Doorenbos and Pruitt 1977;can simulate daily weather data from the monthly meanAllen et al. 1998). A daily water balance is computedof solar radiation, maximum and minimum temperature,using input soil and crop information and ET。Thewind speed, and dew point temperature data to deter-model can use daily observed climate data or it canmine ET。ET, and ETW for 20 crop categories and 4generate simulated daily climate data from monthly dataland-use categories in each of the 10 hydrologic regionsto estimate daily ET。Information from Spatial CIMIS,in Califormia. The ability to change the CO, concentra-which is a model that combines weather station datation was included in Cal-SIMETAW to more accuratelyand remote sensing to provide a grid of ET。informa-estimate the effect of climate change on ET。in additiontion is also used by Cal SIMETAW to estimate nearto changes in temperature and humidity.real-time ET。Cal-SIMETAW is used by DWR to estimate cropevapotranspiration (ET) and evapotranspiration of ap-MODEL DESCRIPTIONplied water (ET ), which is the sum of net irrigationapplications needed to produce a crop. Thus, ET pro-vides an estimate of the water needed to achieve fulling Microsoft C# for numerical calculations, graphics,evapotranspiration in addition to that water supplied byetc. and Oracle software for data storage. In the Cal-preseason soil moisture and in-season effective rainfallSIMETAW project, soil and climate database were devel-assuming 100% application efficiency. Dividing the EToped to spatially characterize ET and ETw Oracle soft-by the mean seasonal application efficiency (AE) pro-ware was used to store the historical daily climate data,vides an estimate of the seasonal water diversions neededi.e, maximum (T) and minimum (T) temperatures andto produce a fully irigated crop. The application effi-precipitation (P ), which were derived from monthlyciency is the ratio of irrigation water applied that con-PRISM data that cover Califonia on a4 kmx4 km grid tributes to evaporanspiration to the total aplied water.spacing. Because the PRISM data are monthly andA first guess for the ET_w would be SET, which is ,daily data are needed to determine ET , daily NCDCthe seasonal total ET。, minus the change in stored soilclimate station data (from October 1921 to Septemberwater during the season and minus any in-season ef-2010), were used with the PRISM data to estimate dailyfective rainfall. Therefore, ET = SET. -SR. -ASW,T, T, and P。The daily climate data development iswhere SR。is the seasonal effective rainfall and ASW=described later in this paper.SW; -SW, is ch' 中国煤化ri'e initial soilA second database containing the soil water holdingwater content (SFontent (SW).capacity and soil depth information was developed from If the seasonalTYHCNMHGCorrectly, the⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1374Morteza N Orang et al.2NA= =SET -SR.-ASW. The Cal-SIMETAW model useshumidity, and wind speed data were lacking from mostcrop, soil, and climate or weather data to determine theclimate data sets prior to development of CIMIS, i.e.,ETw using the sum of a daily soil water balance. Thethe California Irrigation Management Information Sys-generated ETw information provides an estimate of ag-tem (Snyder and Pruitt 1992). Since only tempera-ricultural water demand and thus is important for the ture data were available prior to 1986, it was decidedCalifornia Water Plan.to use daily maximum and minimum temperatures andIn addition to using historical data, the weather gen-the Hargreaves and Samani (1982, 1985) equation toerator in Cal-SIMETAW can simulate regional dailycalculate reference evapotranspiration (ETg) as anweather data from monthly climate data that areapproximation for ET。Using recent climate data fromdownscaled from a GCM“General Circulation Model"CIMIS, comparisons were made between ETHs andto estimate ET。, ET。and ETw . Using crop coefficientET。and calibration factors were developed to esti-data for 20 crop and 4 land-use categories, Cal.mate ET。from ETHs as a function of wind speed andSIMETAW estimates daily ET , SET, and ETg fromsolar radiation. In general, ETHs was lower than ET。2030 and 2050 climate projections for each of the 10under windy conditions and it was higher than ET。hydrologic regions within Califormia for use in the Cali- under calm conditions. Using approximately 130formnia Water Plan.CIMIS weather stations distributed across the state, a4 kmx4 km grid of correction factors for the ETHsPurpose of detailed analysis/County units (DAU/equation was developed. There are many daily tem-Countyperature and precipitation weather stations in Califormia,but the PRISM data set (PRISM Group 2011) pro-DWR has subdivided California into 482 DAU/Counties,vided a long-term GIS data base of historical dailywhich are geographic areas having relatively uniformmaximum and minimum temperature and precipita-ET。throughout the region. The regions are used fortion on the same 4 kmx4 km grid as the correctionestimating water demand by agricultural crops and otherfactor GIS map. Thus, using the PRISM historicalsurfaces for water resources planning. DAUs are basedtemperature data to compute ETs and the calibrationon watershed and other factors related to water trans-factors, Cal-SIMETAW is able to produce ET。esti-fer and use within the region, which are often split bymates on a 4 kmx4 km grid over the state from Octo-counties. DAU/Counties are the smallest study areasber 1921 to September 2010.used by DWR. The largest study areas comprise theten hydrologic regions. Land use surveys are periodi-ET。correction factorscally completed within each DAU/County by DWRstaff, and the percentages of each crop within a mul- NationalClimate Data Center (NCDC) stations were pairedtiple crop/land-use category are recorded for most DAU/with neighboring CIMIS stations from 1986 throughCounty regions. Using the percentages of each crop2010. Corresponding data for the paired stations werewithin a DAU/County, the individual crop coefficientsselected from the University of California Integrated Pestand growth rates are analyzed to determine a weightedManagement (UC IPM) site (t:/ipm.ucdavis.edu). Themean K。curve for each category. Thus, each DAU/daily Penman and Monteith equation was used to calcu-county can have as many as 20 crop and 4 land-uselate reference evapotranspiration (ET ) using daily CIMIScategories with weighted mean K。curves (Fig. 1).data and the HS equation was used to calculate ET。(ET)using daily Ty and T。data. The correction factor (Cp)Reference evapotranspiration(ET。)was calculated as: C= =ET /ETys. Spatial interpolationwas completed using ARC GIS and a 4 km gridded ras-Weather and climate data are commonly used to calcu-ter map for CF was produced (Fig. 2). The CF valueslate standardized reference evapotranspiration (ET) forfell within 15% of 1.0. The CF values were archived forshort canopies (Monteith 1965; Monteith and Unswortheach 4 kmx4 km中国煤化工s were stored1990; Allen et al. 1998, 2005), but solar radiation,in files designatYHCNMHGmber.⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1375Spatial CIMIS ET。programto satisfy the Penman-Monteith ET。equation (Hartet al. 2000).The Califormia Irigation Management Information Sys-tem (CIMIS) is a program developed by UC DavisReal-time Cal-SIME TAWand operated by DWR to help farmers, turf and land-scape managers and other resource managers to de-Cal-SIMETAW provides a method to analyze histori-velop water budgets that improve irrigation schedul-cal data to determine trends in agricultural watering and monitor water stress. CIMIS weather sta-demand, but it is also useful for near real-time detions are located at key agricultural and municipal sitesmand estimates. Although there are about 130 CIMISthroughout Califormia to collect comprehensive, timely,weather stations in California, many locations haveweather data on an hourly basis and to disseminatelimited weather data for ET。estimation, so there arethe weather and ET , data to help farmers and land-gaps in the spatial data. To resolve this problem, DWRscape professionals to improve the efficient use ofand UC Davis used satellite data and developed spatialirrigation water. For the Spatial CIMIS program,CIMIS to estimate ET。on a 4 kmx4 km grid over theweather data collection system is combinedstate. Since the Spatial CIMIS uses the same grid aswith NOAA Geostationary Operational EnvironmentalCal-SIMETAW and it provides near real time ET。Satellite (GOES) visible satellite data to to extend the(i.e., up through the previous day), the output fromreference evapotranspiration (ET) estimates to areasSpatial CIMIS was incorporated into Cal-SIMETAWnot well covered by CIMIS and to provide daily spa-and to develop near real-time daily maps of crop ETc.tial ETo maps. The maps are calculated on a (4 kmx4Spatial CIMIS is available and explained on the CIMISkm) square grid, which is a high spatial resolutionwebsite (CIMIS 2011).when compared to the density of CIMIS stations. Thehourly GOES satellite images are used to estimatecloud cover which are used in turn to modify clearVerification of ET。datasky radiation estimates. These are combined with in-terpolated CIMIS weather station meteorological data Results from Cal-SIMETAW were validated againstHR and DAU/County boundariesSan Francisco BaySouthCoastSacramento RiverSan Joaquin RiverNorth LahontanSouth Lahontan! Colorado RiverDetail Analysis UnitCounty lineCrrection factor: HSto PM ET。1 High: 1.14111Low: 0.821548中国煤化工:Fig. 2 Correction f:ing Hargreaves-Fig. 1 California study area map showing hydrologic regions, detailed Samani ET。(ETH:YHC N M H Gfor California.analysis units (DAU), and counties.ET=HTHSxCF.⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1376Morteza N Orang et al.spatial CIMIS ET。estimates from 2004 to present (Figs.10一Spatial CIMIS3-6).Cal-SIMETAWCIMIS network station measurements are amongthe most reliable direct datasets of daily weather vari-ables including solar radiation (R ), maximum air tem-perature (Tm), minimum air temperature (T), windspeed (U), dew point temperature (T), and etc. Ref-erence evapotranspiration (ET), computed by the daily200420052006(24-h) Penman-Monteith equation, has been recom-Time (d)mended by both America Society of Civil Engineers(ASCE) and United Nation FAO. As a final verifica-Fig. 3 Comparison of daily ET。estimates versus time from Cal-tion of our calibrated Hargreaves Samani equation for SIMETAW and Spatial CIMIS for PRISM grid number 50-60, Januaryestimating ET , a comparison of the calibrated ETHS2004-July 2007.from Cal-SIMETAW and CIMIS-based estimates ofET。with data from Davis, California are shown inFigs. 7-9. The results show that estimates of ET。fory=0.98x1990-2007 closely approximate ET。 values fromR2-0.92冒8CIMIS. The mean ET。estimates from Davis for the看7period of 1990-2007 were 3.90 and 3.94 mm with层6standard deviations of 2.25 and 2.52 mm for the cali-brated Hargreaves-Samani model and CIMIS,respectively. The difference between the two ap-proaches was small (roughly 1%).Crop and land-use categories0↑23↓56789 7oSpatial CIMIS ET。estimates (mmd')Daily soil water balance is the key component of theETgw model. The calculations require input of weather Fig. 4 Comparison between daily ET。estimates from Cal-or climate data, soil depth and water-holding capacity,SIMETAW versus Spatial CIMIS for PRISM grid number 50-60from January 2004 through July 2007.crop root depth, and seasonal crop coefficient curves.Because there are thousands of soil and cropping pat-tern combinations (including differences in cropping soil depth, and rooting depth information for all of Cali-seasons), it is impossible to account for all combina-fornia was developed from the USDA-NRCS SSURGOtion in the state. The biggest limitation is the lack ofdatabase (SSURGO 2011). The developed database cov-both historical and current cropping patterners all of California on the same 4 kmx4 km grid for allinformation. In recent years, however, the croppinglocations that are included in the PRISM database, whichinformation has dramatically improved and refine-covers most of California. There are about 26 300ments are likely in the future. To overcome the prob-PRISM grids in the model's database for California.lem of too many crop and soil combinations, the cropswere separated into 20 crop and 4 land-use catego- Crop cofficientsries that consist of surfaces with similar character-istics (Table 1).Crop evapotranspiration is estimated as the product ofreference evapotranspiration (ET) and a crop coeffi-Soils characteristics and rooting depthscient (K ) value. Cron cnefficients are commonly de-veloped by mea中国煤化工r., and deter-A database containing the soil water holding capacity,mining the rYHCNMHGoftheCal-⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1377240-Spatial CIMIS220- ---- CaI-SIMETAW200-180-160-140-120-100-8060-4020Time (mon-yr)Fig. 5 Comparison of monthly total ET。estimates versus time for Cal-SIMETAW and Spatial CIMIS for PRISM grid number 50-60,January 2004-December 2006.240Calculated from Cal-SIMETAW220 --1.006612------ Obtained from CIMIS200- R2-0.9908190 ]? 10-140 -120 .“80-601990199199219931994Time (d)0十204068010012014016180200220240Fig. 7 Comparison of daily ET。estimates for Cal-SIMETAW andSpatial CIMIS ET。cstimates (mm mon')CIMIS at Davis, California within the PRISM grid 99-62 from1990 to 1994.Fig. 6 Comparison between monthly ET。estimates from Cal-SIMETAW versus Spatial CIMIS for PRSIM grid number 50-60valuesare used to estimate daily K。values during afrom January 2004 to December 2006.season.One of main objectives of this project was to refineSIMETAW crop coefficient values were developed inand improve crop coefficient values for 20 crop cat-California, but some were adopted from Doorenbos andegories on each of the 482 DAU/Counties within thePruitt (1977) and Allen et al. (1998). While crop coef-state using the County Ag Commissioner reportsficients are continuously developed and evaluated, Cal-(CDFA) and DAU boundaries. Crop categories thatSIMETAW was designed for easy updates of both Krepresent individual crops have seasonal crop coeffi-and crop growth information. Also, K。values needcient (K) curves, but categories containing multipleadjustment for microclimates, which are plentiful andcrops do not have a single seasonal K。curve. Usingextreme in California. A microclimate K。correctionthe percentages of each crop within a DAU/County,based on the ET。rate is included in the Cal-SIMETAWthe crop coeffil中国煤化工analyzed tomodel. The K。values and corresponding growth datesdetermine a wiFor each cropfMHCNM HGare included by crop in the model. These dates and Kccategory.⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1378Morteza N Orang et al.Estimated from CaI-SIMETAWObtained from CIMIS1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007Time (mon)Fig. 8 Comparison of monthly mean ET。estimates versus time for Cal- SIMETAW and CIMIS at Davis, California within the PRISM grid99-62 from 1990 to 2007 time period.-1.0087x8about 10 to 75% ground cover, the Kc value increasesR2=0.9725linearly from K B to K C. The K。values are typically a7constant value during midseason, so K C=K, D. Dur-ing late-season, the Kc values decrease linearly fromKD to K E at the end of the season (Fig. 10).Doorenbos and Pruitt (1977) provide estimatednumber of days for each of the four growth periodsto help identify the end dates of growth periods. Be-cause there are climate and varietal differences,however, and because it is difficult for growers toknow when the inflection points occur, irrigators of-Cal-SIMETAW ET。(mm)ten find this confusing. To simplify this problem, per-centages of the season from planting to each inflec-Fig. 9 Comparison of monthly mean ET。for CIMIS versus Cal-tion point rather than days in growth periods are usedSIMETAW at Davis, California within the PRISM grid 99-62 from1990 to 2007.(Fig. 10). Irrigation planners need only enter the plant-ing and end dates and the intermediate dates are deter-mined from the percentages, which are easily storedField and row cropsin a computer program.During initial growth of field and row crops, a de-Field and row crop K。values are calculated using afaultK; =K B=K A unless it is overridden by entering anmethod similar to that described by Doorenbos and initial growth K. based on rainfall or imrigation frequency.Pruitt (1977) and Allen et al. (1998). A generalizedThe values for K C=K D depend on the difference incurve is shown in Fig. 10. In their method, the season (1) light interception, (2) crop morphology effects onis separated into initial (date A-B), rapid (date B-C),turbulence, and (3) physiological differences betweenmidseason (date C-D), and late season (date D-E) the crop and reference crop. Some field crops aregrowth periods. K。values are denoted K A, K B, K C,harvested before senescence, and there is no late sea-K.DandKEattheendsoftheA,B,C,D,andEgrowthson drop in K。(for example, silage corn and fresh mar-dates, respectively. During initial growth, the K。val-ket tomatoes). Relatively constant annual K。values areues are at a constant value, so K A=K B. During thepossible for some crops (for example, turfgrass andrapid growth period, when the canopy increases frompasture) with 1中国煤化工"YHCNMH G .⑥2013, CAAS. AlI ights reserved. Published by EsevierLd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1379Table 1 Crop and land-use category numbers, symbols and descriptionsLand-use Crop symbolSurface category descriptionGGrain (wheat, wheat_ winter, wheat spring, barley, oats, misc._ grain & hay)RIRice (rice, rice. _wild, rice. flooded, rice-upland)CCottonSISugar beet (sugar-beet, sugar_ beet_ late, sugar. beet early)CorrDDry bean:S/SfflowerFIOther field crops (flax, hops, grain_ sorghum, sudan,castor-beans, misc._ field, sunflower, sorghun/sudan_ hybrid, millet, sugarcaneAAlfalfa (alalfa, alfalfa _mixtures, alfalfa cut, alfalfa_ annual)1(P/Pasture (pasture, clover, pasture_ mixed, pasture_ native, misc._ grasses, turf_ farm, pasture_ bermuda, pasture_ rye, klein_ _grass, pasture_ fescue)1TI1:Tomato fresh (tomato fresh. tomato frestCucurbits (cucurbits, melons, squash, cucumbers, cucumbers_ fre:esh_ market, cucumbers_ machine-harvest, watermelon)Onion & garlic (onion & garlic, onions, onions_ dry, onions_ green, garlic)Potatoes (potatoes, potatoes_ sweet)16THTruck_ Crops_ misc (artichokes, truck. _crops, asparagus, beans_ green, carrots, celery, lettuce, peas, spinach, bus h_ berries, strawberries,peppers, broccoli, cabbage, cauliflower)17AlAlmond & pistacios18o1Orchard (deciduous) apples, apricots, walnuts, cerries, peaches, nectarines, pears, plums. prunes, figs, kiwis)19Citrus & subtropical (grapefruit, lemons, oranges. dates, avocados, olives. jojoba)2(Vineyards (grape_ _table, grape. _raizin, grape. wine)21UUrban landscape (cool-season turf, warm- season turf, golf course, open water)22R\Riparian (marsh, tules, sedges, high water table meadow, teese, shrubs, duck marsh)23Native vegetation (grassland, light brush, medium brush, heavy brush, forest, oak. woodland)24Water surface (river, stream, channel delivery, freshwater Jlake, brackish _saline, wastewater)Planting, 10%Cgr 75%Cp/T-01.47100%3-.2-75%.1-50%、0十20%.9-.8-2 0.7-.6-.4-.3-.2十0.0+Mar-04Apr-04May-04Jun-04Jul-04Aug-04Sep-04Oct-04Nov-04Growth date (mon-yr).... Initial stage - . - Rapid growth-Mid-season - .●Late seasonFig. 10 Hypothetical crop cofficient curve for field and row crops using percentage of the season to delineate growth dates. The seasonends when transpiration (T) from the crop ceases (T).Some field crops and landscape plants (type-2 crops)bare soil K。should be used. The bare soil K。valuehave fixed K。values all year. However, if the signifi-serves as a baseline for the crop coefficient, and thecant rainfall frequency is sufficient to have a higher K。higher of the fix中国煤化工K. is used tofor bare soil than for the selected crop, then the higherestimate ETMHCNMHG⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1380Morteza N Orang et al.Tree and vine crop K valuesthan mature crops. The following equation is used toadjust the mature K。values (K。) as a function of per-Deciduous tree and vine crops, without a cover crop,centage ground cover (C).have K. curves that are similar to field and row cropsbut without the initial growth period (Fig. 11). De- .If sinCg. π> 1.0then Kc=Kcm elseI702_faultK. B, K C=K D=K 2 and KcE K 3 values are in-cluded in Cal-SIMETAW. The season begins withK.=Kcmsir「ex. π(1)rapid growth at leaf out when the Kc increases from70 2J_KB to K C. The midseason period begins at approxi-mately 70% ground cover. Then, unless the crop isSubtropical cropsimmature, the K。is fixed between dates C and D, .which corresponds to the onset of senescence. Forimmature crops, the canopy cover may be less thanFor mature subtropical orchards (for example, citrus),70% during the midseason period. If so, the K。willusing a fixed K。during the season provides acceptableET。estimates. If higher on any given date, however,increase from K.C up to the K D as the canopy coverincreases, so the Cal-SIMETAW model accounts fothe bare soil K。replaces the orchard K。For an imma-K. changes of immature tree and vine crops. Duringture orchard, the mature K。values (K ) are adjustedlate season, the K decreases from K D to K E, whichfor their percentage ground cover (C ) using the fol-lowing criteria.occurs when the transpiration is near zero.Initially, the K. value for deciduous trees and vines(K.B) is selected from a table of default values.|sinCg_ π≥1.0then K.=Kcm or else[702However, the ET is mainly soil evaporation at leaf out,so Cal-SIMETAW contains the methodology to deter-(2)|Cg. πmine a corrected K B based on the bare soil evaporation.K.=Kan/sin|70 2Immature deciduous tree and vine crops use less water1.4710%Cq100% :70%1.1-35%0.9-0.8-义0.7-0.6-0.5-0.4-0.3-Leaf out70%CgLeaf drop0.1pI0.0Jan-04 Feb-04 Mar-04Apr-04 May-04Jun-04Ju1-04 Aug-04 Sep-04 Oct-04 Nov-04Growh date (mon-yr)- - Rapid growth- Mid-season - - ●Late seasonFig. 11 Hypothetical crop cofficient curve for deciduous tre and vine crops using per中国煤化工。; growth dates.There is no initial growth period, so the season starts at leaf out on date B.MHCNM HG⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1381Cover crop corrections1.00With a cover crop, the K. values for orchards and vinesy-2.54r00FAO 24 1s. Modelare higher. When a cover crop is present, 0.35 is addedrmse-0.13to the clean-cultivated K。. However, the K. is not al-s 0.60lowed to exceed 1.20 or to fall below 0.90. Cal-SIMETAW allows the beginning and end dates to be0.40entered for two periods when a cover crop is presentin an orchard or vineyard.0.20Estimating bare soil K。values.00120(CET.OS (mm"*)A soil evaporation K. value, based on ET。and rainfallfrequency is needed as a minimum (base line) for esti-Fig. 12 Bare soil crop cofficient curve as a function of the squareroot of CET。.mating ET。It is also useful to determine the K. valueduring initial growth of field and row crops(K。1=K A=K B), based on imrigation frequency, and theDuring the off-season, the bare-soil K。value is usedstarting K。for deciduous tree and vine crops (K 1=K B).to estimate the ET. During the season, the bigger ofThe K。values used to estimate bare soil evaporation arethe bare-soil K. or the K. based on the crop K。values isbased on a two-stage soil evaporation method reportedused to calculate the crop evapotranspiration as:by Stroonsnjider (1987) and refined by Snyder et al.ETc=ET.xK。(5)(2000) and Ventura et al. (2006). The method proFig. 13 presents an example for a tomato crop wherevides a K. values as a function of ETo rate and wetting the bare-soil K (dark line) was higher than the crop K。frequency that are similar to those published in(colored line) during part of the season. The greenDoorenbos and Pruitt (1977). Computation of the barecolored line in Fig. 13 shows a K. curve for a crop thatsoil K。values is somewhat complicated, so a simplifiedhad frequent irrigation after planting that increased themethod was recently developed by comparing the K。K。value during initial growth. In all cases, the highervalues generated using the model from Ventura et al.of the bare-soil and crop K。is used to determine the(2006) with the square root of the cumulative ET. TheET。on each day.results are shown in Fig. 12. Therefore, a good esti-mate of a typical bare soil K : value is obtainable usingEvapotranspiration of applied water(ET2w)Fig.12 shows a bare soil K。curve as a function of thesquare root of the cumulative reference evapotranspi-Irrigation is applied whenever the soil water content onration (CET).a given day would fall below the management allow-To determine the baseline Kc from rainfall frequency,able depletion (MAD) set for that date. The net appli-the (CET )0.s used to determine the bare soil crop coef-cation (NA) amount is the depth of water needed toficient is calculated as:raise the soil water content back to field capacity (FC)(CET)PS=7V DBxET。(3)on the irrigation date. The soil water content on eachday of the season is calculated as:Where DBR is the number of days between rainfallSWC=SWC-Dw+NA(6)events, and ET。is the mean daily ET。rate during thenon-rainfall period. Then, the bare soil K value duringWhere SWC。is the soil water content on the previ-that period is estimated as:ous day, NA is the net application, which is zero onnon-irrigation days, and Dw is the daily change in soil2.54Kc=-(4)water content中国煤化工√CET。Dw=ET-Es,YHCNMH G(7)⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1382Morteza N Orang et al.Mid-scason-- Late season1.2-0.50.8-0.7-0.6-, 0.0.4-0.3-0.1-0.0Dct-95 De-95 Feb-96 Mar-96 May-96 Ju1-96 Aug_-96 Oc1-96 De-96 Jan-97 Mar-97 Apr-97 Jun-97 Aug-97 Sep-97Time (mon-yr)Fig. 13 Daily calculated bare soil and crop cofficient values with different colored lines for each growth period for currently entered dailyweather and crop/soil information during the growing season and off-season.Where ET。is the evapotranspiration and E and E, Water balance calculationsare the seepage and effective rainfall contributions tothe soil water reservoir.Although Cal-SIMETAW has soil characteristic infor-ETw is the amount of applied irigation water thatmation and computes ET。on a 4 kmx4 km grid, cropcontributes to ET:; therefore, ETw is the sum of the netplanting information is limited to the DAU/County.irrigation applications during a cropping season. TheTherefore, the DAU/County is the smallest unit for cal-ET for “n”irrigation events is therefore calculated as:culation of the water balance and thus ETw for a par-ticular crop or land-use category and soil combinationETaw=NA:+NA-+..+NAn-2NA;(8)for each DAU/County. Using GIS, a weighted meanAlternatively, ET can be calculated as the seasonalvalue is determined by DAU/County for the soil waterholding characteristic, soil depth, root depth, and ET。total evapotranspiration (SET) minus the cumulativeThe smaller of the soil and root depth and the weightedseasonal effective seepage contribution (SE。) minusthe cumulative seasonal effective rainfall contribution(SE, ) minus the difference in soil water content (OWC)900.sWC-iference betvccn itial and final soil water conent800 -from the beginning to the end of the season (Fig. 14):SEpy+SE,=154+66700 -SET。SET:=806ETw=(SET-SEp-SE)-OWC600.500--- SDt WC-30The cumulative seasonal D.w curve (SD, w) is com-..●SEpsTw "400 .puted as:300-E,SDsw= SETE-Ep-SE,(10)SEp-154 mm100 .Therefore, another expression for ETw is:SE,-660ETw-SDsw-OWC(11)100Fig. 14 ilustrates how one can determine ET fromTime (d-mon)SET, SE, p, SE, SD and ASW. Cal-SIMETAW uses中国煤化工the sum of the net applications (eq. (8)) to determineFig. 14 A plot o:MYHCNM HG'rsus time for aETgw .tomato crop to il⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1383mean water holding characteristics are used to deter-based on longer than daily water balance calculations.mine the plant available water (PAW). A 50% allowableFig. 15 shows a water balance plot for cotton includingdepletion is used to estimate the readily available water the P., NA, FC, PWP, SWC, SWC , and ET, where(RAW) for the effective rooting zone. A managementSWC, is the water content corresponding to the lowerallowable depletion (MAD) is determined by compar- limit of the readily available water.ing the RAW with the cumulative ET。during the season.The MAD is always less than or equal to RAW, and it isVerification of water balance calculationsset so that the soil water content at the end of the sea-son is between RAW and PAW.As a final verification of the Cal-SIMETAW model, weA crop coefficient curve is determined for each cropalso compared our model predictions of annual ETwor land-use category based on the percentages of indi-for tomato, almond, alfalfa, and avocado crops with anvidual crop planting areas within that category. Theindependently derived model called Integrated Waterweighted category K. curves are used with the daily ET。Flow Model (IWFM), which is a water resources man-estimates to calculate daily ET。for the DAU/County Thagement and planning model that simulates groundwater,ET。is subtracted from the soil water content on eachsurface water, stream-groundwater interaction, andday until the soil water depletion (SWD) exceeds theother components of the hydrologic system (Dogrul et al.MAD. Then an irrigation is applied and the soil water2011). IWFM simulates stream flow, soil moisturedepletion goes back to zero (i.e, back to field capacity).accounting in the root zone, flow in the vadose zone,Similarly, rainfall will decrease the soil water content toas high as field capacity, but not higher. Rainfall is onlygroundwater flow, and stream-aquifer interaction. Ag-effective up to a depth equal to SWD, so effective rain-ricultural and urban water demands can be pre-specified,fall cannot exceed the SWD before the rainfall. There isor calculated intermally based on different land use typesno correction for runoff or runon to the field. It is as-(Table 2).sumed that rainfall that results in runoff will likely fill thesoil to field capacity, and the assumption that effectiveWeather simulationrainfall cannot exceed SWD still applies. This effectiverainfall estimation method works because the water bal-Weather simulation models are often used in conjunc-ance calculations are daily. It might fail for for models tion with other models to evaluate possible crop re-600 7-Pcp-eNA-FC一-PWP一-SWC一SWCx一ETcr 260550 -240220450 -00400 -180160一14300 -120 ”250 -t 100旁200-十80150 -t6出0-40十2otTime (mon-yr)中国煤化工Fig. 15 Fluctuations in soil water content of a cotton crop using a daily water balance.MHCNMH G⑥2013, CAAS. AlI ights reserved. Published by EsevierLd.1384Morteza N Orang et al.sponses to environmental conditions. One important high wind speed values generated for use in ET。response is crop evapotranspiration (ET). Crop evapo-calculations. Because wind speed depends on atmo-transpiration is commonly estimated by multiplying ref-spheric pressure gradients, no correlation between winderence evapotranspiration by a crop coefficient. In Cal-speed and the other weather parameters used to esti-SIMETAW, climate or projected data are used to esti-mate ET。exists. Therefore, the random matching ofmate daily reference evapotranspiration. Rainfall datahigh wind speeds with conditions favorable to highare then used with crop and soil information and esti-evaporation rates leads to unrealistically high ET。esti-mates of ET。to determine ETw One can either usemates on some days. To eliminate this problem, anobserved or simulated daily data for the calculations.upper limit for simulated wind speed was set at twicethe mean wind speed. This is believed to be a reason-Rainfallable upper limit for a weather generator used to esti-mate ET。because extreme wind speed values are gen-Characteristics and patterns of rainfall are highly sea-erally associated with severe storms and ET。is gener-sonal and localized; it is difficult to create a general, sea-ally not important during such conditions.sonal model that is applicable to all locations. Recogniz-ing the fact that rainfall patterns are usually skewed toTemperature, solar radiation, and humiditythe right toward extreme heavy amount and that rainstatus of the previous day tends to affect the present dayTemperature, solar radiation, and humidity data usuallycondition, a gamma distribution and Markov chain mod-follow a Fourier series distribution. A model of theseeling approach was applied to described rainfall patternsvariables is expressed as:for periods within which rainfall patterns are relativelyXk=u2(1+δCx)kuniform (Gabriel and Neumann 1962; Stern 1980; LarsenWhere k=1, 2 and 3 (k=1 represents maximumand Pense 1982; Richardson and Wright 1984). Thistemperature; k =2 represents minimum temperature;andapproach consists of two models: two-state, first order k= =3 represents solar radiation), Hr is the estimated dailyMarkov chain and a gamma distribution function. Thesemean, and C; is the estimated daily coefficient of varia-models require long-term daily rainfall data to estimatetion of the ith day, i=1, 2, .... ,365 and for the kthmodel parameters. Cal-SIMETAW, however, usesvariable.monthly averages of total rainfall amount and number ofCal-SIMETAW simplifies the parameter estimation pro-rain days to obtain all parameters for the Gamma andcedure of Richardson and Wright (1984), requiring onlyMarkov Chain models (Geng et al.1986).monthly means as inputs. From a study of 34 locationswithin the United States, the coefficient of variability (CV)Wind speedvalues appear to be inversely related to the means. Thesame approach is used to calculate the daily CV values. InThe simulation of wind speed is a simpler procedure,addition, a series of functional relationships were devel-requiring only the gamma distribution function as de-oped between the parameters of the mean curves and thescribed for rainfall. Although using a gamma distribu-parameters of the coefficient of variation curves, whichtion provides good estimates of extreme values of windmade it possible to calculate C; coefficients from μ; curvesspeed, there is a tendency to have some unrealisticallywithout additional input data requirement.Climate changeTable 2 A comparison of ET calculated with IWFM and Cal-SIMETAW models fcor tomato,almond, alfalfa, and avocado cropsgrown in CaliforniaThe ability to make preliminary adjustment for climateCropIFWF(mm)Cal-SIMETAW (mm)change impacts on evapotranspiration and more im-Tomato697750portantly watq! in the Cal-Almond1010.中国煤化工Alfalfa340338SIMETAW moweather gen-Avocado6955erator that simuYHCNMHGlaily weather⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1385data from input monthly means.Statistics from theobserved daily weather data from the Davis CIMIS sta-generated data are nearly identical to observed data. Thtion were used in the model to calculate monthly meanssimulated data are treated like observed data to computethat were then used to simulate 30 years of daily weatherET。and estimate ET。To study climate change, onedata. The weather data consist ofR, Tmax; Tmn, U,Tyonly needs to change the monthly mean climate variablesand P。。The weather data simulated from Cal-SIMETAWto the projected climate. The program adjusts forwere compared with the observed data from CIMIS. Figsradiation, temperature, humidity, wind speed, and car-17- 23 ilustrate that all Cal-SIMETAW simulated variablesbon dioxide concentration. Of course, a bigger effectand ETo were well correlated with CIMIS observations.on irrigated agriculture is the expected change inThe performance of Cal- SIMETAW was also evaluated atprecipitation. Changing the input monthly precipitationusing data from Bishop, which is influenced by a windydata will modify precipitation patterns, and Cal-SIMETAWdesert environment on the easterm side of the Sierra Ne-will indicate if the demand for irrigation water will changevada Mountain Range, and with data from Oceanside,due to the precipitation changes. Thus, Cal-SIMETAWwhich is a coastal site in San Diego County.does allow for the input of projected climate change andit will provide information on agricultural water demandAgricultural energy use in Californiain the new scenario. The weather generator in Cal-SIMETAW model allows us to investigate how climateCaliformia agriculture is a multibillion dollar industry, thechange could affect the water demand in the state. Fornumber one producer in the nation, and the largest con-example, by increasing or decreasing the monthly solarsumer of both water and energy. Most of the energyradiation, temperature, and/or dew point temperature,used by agriculture irrigation goes to pump groundwater.the impact on ET。, ET, and ET is easily assessed. ThAccording to the California Energy Commission, Cali-simulation program also allows us to vary CO, concen-fornia growers use about 20 percent of the total U.S.tration (ppm) to investigate the effects of increasing CO,agricultural electricity, or about 10000 GWH per yearconcentration on ET。Since the weather generator infor irrigation. The agricultural energy demand is highCal-SIMETAW simulates daily from monthly rainfall data,and peaking because surface water supplies are limitedit also offers the ability to determine the impact of changingand pumping groundwater for irrigation is growing.rainfall patterns on the water balance and ET.Some of the factors causing for the increases in agri-Using monthly mean data from Davis, California, thecultural energy use, are the intensive use of groundwa-Cal-SIMETAW simulation model was run using fourter storage and drip and micro-sprinkler (drip/micro)scenarios: (1) no changes to the current monthly meandata; (2) all monthly maximum and minimum tempera-tures were increased by 3°C; (3) the same scenario as 2,07 一. +Air and dew Pt temperaturebut also increasing monthly mean dew point tempera-Air temperature and CO2 concentrationture by 3°C; (4) the same scenario as 3, but also increas-ing the CO2 concentration from 372 to 550 ppm. Rela-Mtive to scenario 1, the mean daily ET。rates for an aver-age year increased 18% (scenario 2), 8.5% (scenario 3),and 3.2% (scenario 4). A plot of the mean over 30 yearsof the simulated scenario data is shown in Fig. 16. Thisexample shows that increases in dew point and CO, con-centration can at least partially offset increases in ET。resulting from higher air temperature.0731619112151181211241271301331361Day of the year (d)Simulation accuracyFig. 16 Comparis中国煤化工。; four differentTo test the accuracy of Cal SIMETAW, 29 years of scenarics at Davis,:YHCNM HG⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1386Morteza N Orang et al.- Simulated by Cal-SIMETAW4.5ηSimulated by Cal-SIMETAWObtained from CIMIS. Obtained from CIMIS4t30 -s-25-2.5-E 20-15s-"10-0.5-o+i 316191121151181211241271301331361316191121151181211241271301331361Day of the year (d)Fig. 20 Comparison of measured and simulated daily wind speed atDavis, California.Fig. 17 Comparison of observed and simulated daily solar radiationat Davis, California.12-0ηSimulated by CaI-SIMETAW5H10.0-4"hoDay ofthe yer(d)T316191211518121241271301331361Fig. 21 Comparison of measured and simulated daily dew pointtemperature at Davis, California.Fig. 18 Comparison of measured and simulated daily maximum air. Simulated by CaI-SIMETAW8、7 .16 1- Simulatedd by Cal-SMETAW/12.131619112115118121124127130133136113161912181211241271301331361Day. of the year(d)Fig. 22 Comparison of estimated and simulated daily referenceevapotranspiration (ET。) from CIMIS and Cal-SIMETAW at Davis,Fig. 19 Comparison of measured and simulated daily minimum air California .2011 indicated that drip/micro irrigation systems nowirrigation systems. The latest statewide irrigation meth-cover some 3.2 I中国煤化Ind. Becauseods survey conducted by DWR and UC Davis duringof changes in cnYHC N M H Gvers through-⑥2013, CAAS. Alights reseved. Published by EsevierLtd.California Simulation of Evapotranspiration of Applied Water and Agricultural Energy Use in California1387livestock producers. From 1972 to 2010, the area-0.997xplanted has increased from 15 to 30% for orchards andR2-0.9791from 6 to 15% for vineyards. The area planted to veg-etables has remained relatively static, while that plantedto field crops has declined from 67 to 41 % of the irri-gated area. The land irigated by low-volume (drip andmicro-sprinkler) irrigation has increased by about 38%,while the amount of land irrigated by surface methods宫2has decreased by about 37%. Sprinkler usage has de-creased in orchards and vineyards, but it increased in012789vegetable crops. As a result of these trends in irrigationDaily CIMIS ET。(mm)methods, the adoption and usage of ET information forscheduling has increased considerably.Fig.23 Cal-SIMETAW estimates of ET。from simulated climatevariables and ET。fbserved climate data from Davis, CaliforniaCIMIS station.Ways to increase the efficient use of water andenergy resources in agricultureout the California are now switching to drip/micro ir-rigation systems to increase production, reduce laboris important forcosts, and conserve water. Such systems enable farm-maximizing agricultural production and profits per unit ofers to decrease their need for water, but at the cost ofwater and energy used. Water and energy use efficiencyincreased energy use. At the same time, farmers arecan be achieved through the use of optimum irrigationusing groundwater storage more intensively than in thewater management strategies. An optimum irrigationpast. California State Water Project (SWP), which isscheduling, using soil water balance methods minimizesmaintained and operated by DWR, is also the state's largestrunoff and percolation losses, which in turn maximizesuser of power. It uses about 40% of its total powerprofit and optimizes water and energy use. Other solu-consumption to lift the water over the mountains to reachtions include: (1) reducing non-profit evapotranspiration;Southerm California which lacks adequate local water(2) improving on farm-irrigation systems and water sup-resources. About 80 percent of the water carried bypliers systems; (3) using alternative energy sources suchas solar and wind power in pumping groundwater forSWP is used for agriculture in the San Joaquin valley.imigation use; and (4) improving management of surfaceand groundwater storage to better manage the energySurvey of irigation methods in Californiaand water associated with water storage.Reliable information on irigation methods is importantfor determining agricultural water demand trends.CONCLUSIONTherefore, DWR and UC Davis conduct a study every10 years to collect information on irrigation methodsThe Cal-SIMETAW model determines effective rainfallthat were used by growers to irrigate their cropsand evapotranspiration of applied water (ET_v) for crop(Stewart 1975; Snyder et al. 1996; Orang et al. 2008;and land-use categories, which include similar agricul-Tindula et al.2013). The results are compared to ear-tural crops and other surfaces, by AAU/County regionslier surveys to assess trends in cropping and irrigationhaving similar ET。rates within Califormia. The modelmethod. A one-page questionnaire was developed touses daily observed or simulated climate data to ac-collect information on irrigated land by crop and iriga-count for ET losses and water contributions from seep-tion method. The questionnaire was mailed to 10000age of groundwater, rainfall, and irrigation on a dailygrowers in California that were randomly selected frombasis over the中国煤化工a daily watera list of 58 000 growers by the Califormia Departmentbalance. The nclimate dataof Food and Agriculture, excluding rice, dry-land, andor daily climat(MHcNMHGnthlydatato⑥2013, CAAS. Alights reseved. Published by EsevierLtd.1388 _Morteza N Orang et al.Another feature is that Cal-evapotranspiration. Journal of Irrigation and DrainageSIMETAW can employ near real-time ET。informationEngineering, 108, 225-230.from Spatial-CIMIS, which is a model that combinesHargreaves G H, Samani Z A.1985. Reference cropevapotranspiration from temperature. Appliedweather station data and remote sensing to provide aEngineering in Agriculture, 1, 96-99.grid of ET。information over the state. Cal-SIMEATWHart Q J, Brugnach M, Temesgen B, Rueda C, Ustin S L,Frame K. 2009. Daily reference evapotranspiration forcomputes weighted mean daily crop coefficient factors,California using satellite imagery and weather stationcrop evapotranspiration, soil water balance, effectivemeasurement interpolation. Civil Engineering andseepage of groundwater, and effective rainfall for 20Environmental Systems, 26, 19-33.crop categories and 4 land-use categories within eachLarsen G A, Pense R B.1982. Stochastic simulation of daily climatedata for agronomic models. Agronomy Joumal, 74, 510-514.of the 482 DAU/Counties regions within California.Monteith J L.1965. Evaporation and environment. In: 19thThen, using the surface areas, volumes of water corre-Symposia of the Society for Experimental Biology.sponding to crOP evapotranspiration and evapotranspi-University Press, Cambridge. pp. 205-234.ration of applied water are computed for each cropMonteith J L,Unsworth M H. 1990. Principles ofcategory by DAU/County to provide water deman in-Environmental Physics. 2nd ed. Edward Arold, London.formation that helps the state decide on water supplyOrang M N, Matyac S, Snyder R L.2008. Survey of irigationmethods in California in 2001. ASCE Journal ofand distribution needs and solutions. Finally, theIrrigation and Drainage Engineering, 134, 96- 100.weather generator provides the opportunity to investi-PRISM Group. 201 1. Monthly PRISM Climate Data. [201 1-gate possible effects of climate change (e.g.,11-05]. htp://prism.oregonstate.edutemperature, CO2 concentration increases, and rainfallRichardson C W, Wright D A.1984. WGEN: a Model forGenerations Daily Weather Variables. USDA-ARS-8,patterns) on water demand. This information is ex-Springfield, VA.tremely important for DWR to develop plans for waterSnyder R L, Geng S, Orang M, Sarreshteh S. 2012. Calculationand simulation of evapotranspiration of applied water.supply and distribution across the state.Journal of Integrative Agriculture, 11, 489-501.Snyder R L, Plas M A, Grieshop J I. 1996. Irrigation methodsAcknowledgementsused in California: grower survey. Journal of Irrigationand Drainage Engineering, 122, 259-262.The study was supported and funded by the CaliforniaDepartment of Water Resources (DWR).Estimating evaporation from bare or nearly bare soil. Joumalof Irrigation and Drainage Engineering, 126, 399-403.ReferencesSnyder R L, Pruitt W O. 1992. Evapotranspiration dataAllen R G, Pereira L S, Raes D, Smith M. 1998. Cropmanagement in California. In: Irrigation and DrainageSession Proceedings Water Forum 1992. Baltimore,evapotranspiration: guidelines for computing crop waterMD, USA. pp. 128-133.requirements. In: FAO Irrigation and Drainage Paper 56.United Nations-Food and Agricultural Organization, Rome.Stewart JI.1975. Irigation in Califomia: A report to the StateWater Resources Control Board. Standard AgreementAllen R G, Walter I A, Elliott R L, Howell T A, Itenfisu D,Jensen M E, Snyder R L. 2005. The ASCE StandardizedNo.2-2-65. University of California and the CaliforniaReference Evapotranspiration Equation. AmericanWater Resources Control Board, Sacramento, CA.Society of Civil Engineering. Reston, Virginia. p. 192.Sterm R D.1980. The calculation of probability distributionCIMIS. 2011. Spatial CIMIS. [2010-1 1-05] htp://wwcimis.for models of daily precipitation. In: Archiv firwater. ca. gov/cimis/cimiSatOverview.jspMeteorologie, Geophysik und Bioklimatologie (SerieDoorenbos J, Pruitt W O.1977. Guidelines for predictingB). vol. 28. Spring-Verlag, New York. pp. 137-147.crop water requirements. In: FAO Irrigation anStroosnijder L.1987. Soil evaporation: test of a practicalDrainage Paper 24. United Nations-Food anapproach under semi-arid conditions. NetherlandsAgriculture Organization, Rome. p. 144.Journal of Agricultural Science, 35, 417-426.Dogrul EC, KadirT N, Chung F I.2011. Root zone moistureSSURGO.2011. Soil Survey Geographic (SSURGO)routing and water demand calculations in the contextDatabase. USDA NRCS. [2010-05-06]. htp://soils.usda.of integrated hydrology. Journal of Irrigation andgov/survey/geography/ssurgo/Drainage EngineeringTindula G N, Orang M N, Snyder R L. 2013. Survey ofGabriel K R, Neumann J.irrigation methods in California in 2010. ASCE Journaldaily rainfall occurrence at Tel Aviv. Quarterly Journalof Irigation and Drainage Engineering, 139, 233-238.of the Royal Meteorological Society, 88, 90-95.Ventura F, Snyder R L, Bali K M.2006. Estimating evaporationGeng S, Penning de Vries F W T, Supit I. 1986. A simplefrom bare soil using soil moisture data. Journal ofmethod for generating daily rainfall data. AgriculturalIrrigation ar中国煤化工2, 153-158.and Forest Meteorology, 36, 363-376.CNMH GHargreaves G H, Samani Z A.1982. Estimating potential3UN Lu-juan)⑥2013, CAAS. Alights reseved. Published by EsevierLtd.
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