Description of cropping systems, climate, and soils
Annual crop production area in the United States of America (USA) occupies 97 million ha. Major crops are maize, soybean, wheat, and rice, which account for 87% of total crop area, and the country is one of the largest producers and exporters of these crops. During the last decade (2009-2018), the USA accounted for 35 of global annual maize and soybean productions.
Table 1. Average (2009-2018) total production, harvested area, and average yield of maize, soybean, and wheat in USA. Source: FAOSTAT
Total production (Mt)
Harvested area (M ha)
Maize-soybean crop systems
More than 85% of maize and soybean is produced in the north-central region known as the ‘Corn Belt’, where continuous maize (≈35%) and 2-year maize–soybean rotation (≈65%) are the dominant cropping systems. The central and eastern regions of the Corn Belt have favorable climate for rainfed crop production, with total annual rainfall that ranges from 800 to 1100 mm. The western edge of the Corn Belt has less rainfall and includes the eastern Great Plains states of North Dakota, South Dakota, Nebraska, and Kansas. Irrigated maize and soybean account for ca. 10-15% of the national production of these crops and their area concentrated in the western fringe of the region. Irrigated soybean is also produced along the Mississippi River valley (mainly in the state of Arkansas). In the Corn Belt, soils are generally deep, fertile, rich in organic matter, and have large water holding capacity in the rootable soil depth (i.e., > 200 mm plant available water). Dominant soils correspond to the Mollisols and Alfisols orders. A detailed description of weather, soil, and cropping systems can be found in Connor et al (2011) and Grassini et al. (2014). In wet years, transient early-season waterlogging is likely in soils with moderate-to-low infiltration rates in the central and eastern regions of the Corn Belt, where subsurface tile drainage is currently used on about one-third of total cropland to mitigate this problem (Sugg, 2007). In the past 60 years, there has been a shift from continuous maize under conventional tillage to a 2-year maize–soybean rotation under some form of conservation tillage (defined as any tillage method that leaves at least 30% of soil surface covered by plant residues). Of total area sown with maize and soybean, 52 and 75% is produced using conservation tillage, respectively (Horowitz et al., 2010). Almost all soybean area in the Corn Belt is sown with transgenic cultivars and the vast majority of those cultivars possess a transgene that provides tolerance to glyphosate. The use of glyphosate-resistant cultivars has provided near-total weed control (though glyphosate-resistant weeds are now increasingly appearing), and has accelerated producer adoption of conservation and no-tillage practices and narrower row spacing. Use of transgenic Bt maize with resistance to a number of damaging insect species is also widespread.
There are three main wheat growing regions in the US, each with its own characteristic and growing different wheat classes. The Great Plains accounts for ~64% of US wheat production and is commonly divided into two regions: the northern (Montana, North Dakota, South Dakota, Wyoming and Nebraska) and southern Great Plains (Colorado, Kansas, Oklahoma, and Texas), accounting for ca. 33% and 31% of the wheat US production, respectively (USDA-NASS, 2015-2019). The southern Great Plains accounts for 57% of the total US winter wheat production and the most widely cultivated wheat class is high quality hard red winter wheat (USDA CDL 2017). The northern Great Plains represents 73% of the total US spring wheat production and the most widely cultivated wheat class is hard red spring wheat (USDA CDL 2017). In eastern US, about 2.3 Mha are sown to soft red winter wheat every year, which is a wheat class used for confectionary products like cookies and crackers. There are two additional minor wheat growing regions in the US, including the Pacific Northwest (hard red spring wheat and soft white winter wheat) and the Californa/Arizona desert (high quality durum wheat). This yield gap analysis focused on the northern and southern Great Plains, as well as the eastern U.S., which altogether account for 76% of US wheat harvested area.
Winter wheat is sown in autumn (Sep-Oct), reaching maturity in mid-summer (June-July) and spring wheat is sown early spring (Apr-May) and reaches maturity during late summer (Aug-Sep). There are strong latitudinal gradients for temperatures and longitudinal gradients for precipitation, elevation, and reference evapotranspiration in the southern Great Plains (Lollato et al., 2017). In comparison, the northern Great Plains have lower winter temperatures, which hamper winter wheat survival; and cooler summer temperatures, which allows for cultivation of spring wheat which goes through the reproductive stages during the summer. Due to the aforementioned weather gradients, the role of wheat within the cropping system changes considerably depending on the region within the US. In the central Kansas and north-central Oklahoma, wheat follows either soybean, maize, or a summer fallow (continuous wheat). Wheat following soybean has a delayed sowing and reduced yield potential (Staggenborg et al., 2003). Wheat following Maize or continuous wheat can be sown around the optimal time in this region, but is more exposed to Fusarium head blight and leaf spotting diseases. In western Kansas, Colorado, and the Oklahoma panhandle, wheat is grown following a long-term (14-month) fallow, a summer fallow, or continuously after maize (Peterson et al., 1996). These previous summer crops or fallow periods were simulated to account for the available water at sowing for the wheat crop. From central Oklahoma into Texas panhandle, about half of the winter wheat is grown as a dual-purpose crop, which is sown 3-4 weeks earlier than for grain-only using higher seeding rates, and grazed by cattle during the winter and early spring, usually yielding about 14% less than a grain-only wheat (Edwards et al., 2011). This system was not simulated as it would either require an animal growth and development model or include coarse assumptions. While the production system is much more diverse in the northern Great Plains, especially in North Dakota, the spring wheat is sown after a winter fallow and therefore we did not simulate a previous summer crop, only simulating the soil water dynamics during the preceding fallow. In Ohio, winter wheat is mainly cultivated in rotation with soybean.
Rice crop systems
U.S. rice production can be split into three ecological zones, the Upper Sacramento Valley (CA), the Gulf Coast (TX, LA, and parts of MS), and the Mississippi River Valley (AR, MO, and parts of MS) (Livezey and Foreman, 2004). Although each of these regions has unique climate characteristics, the climate in the two Southern regions is generally humid with a small range of diurnal temperature variation compared to the climate in CA, which is generally arid/semiarid with large diurnal temperature variation. CA growers use primarily medium-grain temperate japonica rice varieties, whereas growers in the Southern regions primarily use long-grain tropical japonica and hybrid rice varieties. The use of hybrids and herbicide resistant varieties is increasing in the Southern U.S. since roughly 2001, while CA still uses primarily conventional inbred varieties. U.S. rice production systems are direct seeded; CA rice is primarily water-seeded (i.e. – pre-soaked seed is applied to flooded fields via airplane), whereas Southern U.S. rice is primarily drill-seeded. Furthermore, in the southern U.S., rice systems are often rotated with other crops (i.e. soybean and maize) while in CA, due to poorly drained heavy clay soils not suitable for other crops, most rice systems are continuous rice.
Data sources and assumptions
Harvested area and actual yields
The SPAM harvested area maps were used for selecting the reference weather stations for each crop and water regime case. County-level data on crop harvested area and average yields for each crop were retrieved from the USDA-NASS quick stats (http://www.nass.usda.gov/Quick_Stats/). Statistics from 10 cropping seasons were used to calculate average yields for maize (2005-2014), for soybean and wheat (2009-2018) and from five cropping seasons (2010-2014) for rice.
Weather data and reference weather stations
For rainfed and irrigated maize and soybean, historical (last 20+ years) measured daily weather data, including solar radiation, maximum and minimum air temperature, precipitation, relative humidity and wind speed were obtained from the High Plains Regional Climate Center (HPRCC), the Illinois Water and Atmospheric Resources Monitoring Program (WARM), Ohio Agricultural Research and Development Center (OARDC) Weather Service, the University of Wisconsin Extension Ag Weather, the Indiana Purdue Automated Agricultural Weather Station Network (PAAWS), North Dakota Agricultural Weather Network (NDAWN), Michigan State University Enviro-Weather, Oklahoma Mesonet, State Climate Office of North Carolina (SCO), West Texas Mesonet, the University of Minnesota Southern and Southwest Research and Outreach Centers, the South Dakota Climate and Weather, the Missouri Mesonet (AgEBB), and the Texas A&M Integrated Agricultural Information and Management System (iAIMS) Climatic Database †. Meteorological stations selected from these networks are located in agricultural areas, rather than in urban areas, which helps to ensure the representativeness of the weather data for estimating yield potential. Due to the lack of high-quality measured weather data, we used gridded daily weather data from the NASA Prediction of Worldwide Energy Resource (POWER; http://power.larc.nasa.gov/) for one location in TX (Draughon Miller).
For wheat historical (last 20+ years) measured daily weather data, including solar radiation, maximum and minimum air temperature, precipitation, relative humidity were obtained from the High Plains Regional Climate Center (HPRCC), North Dakota Agricultural Weather Network (NDAWN), Montana Mesonet, Oklahoma Mesonet, Colorado Mesomet, and the Texas A&M Integrated Agricultural Information and Management System (iAIMS) Climatic Database. Similar to maize and soybean, these stations are located in primarily agricultural rather than urban areas.
For irrigated rice, historical (last 13 to 15 years) measured daily weather data included maximum and minimum air temperature, precipitation, relative humidity, and wind speed. Data were retrieved from the California Irrigation Management Information System (CIMIS), the National Weather Service (NWS) station network, the Louisiana Agriclimatic Information System, the Delta Agricultural Weather Center, and the Texas A&M Integrated Agricultural Information and Management System (iAIMS) Climatic Database. Similar to maize, soybean and wheat, these stations are located in primarily agricultural rather than urban areas.
Quality control and filling/correction of the weather data was performed based on GYGA weather protocols and comparison against weather records from adjacent National Weather Service-Cooperative Observer Network (NWS-COOP) meteorological stations. NASA-POWER was used as source of incident solar radiation data to fill missing solar radiation data. Hence, complete long-term weather records were available for simulating yield potential (Yp) for irrigated crops and water-limited yield potential (Yw) for rainfed crops.
Based on crop harvested area distribution and the agro-climatic zones defined for USA (Van Wart et al., 2013a), a total of 21 and 45 reference weather stations (RWS) were selected for irrigated and rainfed maize, while a respective 14 and 41 RWSs were selected for irrigated and rainfed soybean, following van Bussel et al (2015). A total of 35 RWS were selected for wheat and 14 for rice. RWS buffer zones accounted for 59 and 55% of total harvested area for irrigated and rainfed maize, 56 and 55% of total harvested area for irrigated and rainfed soybean, 43% for rainfed wheat and 87% for irrigated rice. The agro-climatic zones where these locations were located accounted for 77, 75, 73, 77, 61% and 92% of national area for these crop-water regimes combinations.
For rainfed crops, the dominant soil series were identified for each RWS buffer based on gSSURGO soil database (NRCS, Soil Survey Staff). Briefly, maize and soybean harvested area within each soil type within each RWS buffer was calculated and we included as many soil types as needed to cover ≥50% maize and soybean area within each buffer. Rooting depth was set at 1.5 m for all soil types due to the lack of physical and chemical constrains to root growth and based on observed soil water extraction patterns for maize and soybean (Payero et al., 2006; Ordoñez et al., 2018).
Crop system and management information for crop simulations
Management practices were obtained for each RWS buffer zone. Average sowing date was retrieved from USDA-RMA, while data on cultivar maturity were provided by seed companies and local agronomists. Requested information include: dominant crop rotations and proportion of each of them to the total harvested area, average sowing dates, dominant cultivar name and maturity, and actual and optimal plant population density. The provided data were subsequently corroborated by other local and national experts. Further details on management input data can be found in Morell et al. (2016).
Simulations using maturity of the most widely used cultivar for the region surrounding each RWS were performed using Hybrid-Maize model (Yang et al., 2004). The model was previously validated for its ability to simulate maize yield potential across a wide range of environments in the Corn Belt (Grassini et al., 2009; Liu et al., 2005) and found to be robust at portraying key G x E x M interactions across a wide range of yields, ranging from 0.5 to 18 Mg ha-1. The model does not require site-specific parameter calibration for simulating yield potential, that is, all model parameters governing photosynthesis, respiration, leaf area expansion, light interception, biomass partitioning, and grain filling rate and duration are generic (Yang et al., 2004).
To account for differences in initial soil water at sowing time among years, simulations of rainfed crops were initiated at immediately after harvest of the prior crop assuming 50% of plant available soil water based on Grassini et al. (2009). Soil surface residue coverage at harvest of the prior crop was set at 50% to reflect the large amount of non-grain aboveground biomass left by previous crop and the large proportion of maize production area under no-till or conservation tillage practices (Horowitz et al., 2010). Surface runoff was assumed negligible to reflect producer preference for avoiding highly sloping land for maize production, and wide adoption of conservation tillage and no-till practices, which greatly reduce runoff. Because dominant crop rotations are 2-y soybean-maize and continuous maize, maize yield potential was simulated for all the years for which weather data were available. Because there is little (if any) difference between actual and optimal plant population, the simulations were based on the range of optimal plant population reported for each buffer zone by the local agronomists. Simulations assumed no limitations to crop growth by nutrients and no yield reductions due to weeds, pests, and diseases.
A factor that is not accounted for by the crop simulation model, with a likely positive impact on rainfed yields (especially in drought years), is the water supply from perched water tables in the central and eastern regions of the Corn Belt. Five independent sources of information were used to identify RWS buffers with likely influence of perched water tables on water-limited yields: (i) data on depth to water table from gSSURGO (NRCS Soil Survey Staff), (ii) maps on subsurface tile-drained area distribution in USA (Sugg, 2007), (iii) consultation with local agronomists, (iv) data from shallow groundwater wells networks (e.g., http://isws.illinois.edu/warm/groundwater/), and (iv) trends in actual yield at these locations (i.e., high yields with little year-to-year variation despite contrasting differences in rainfall). Following this approach, we identified 19 RWS buffer zones in the central and eastern regions of the Corn Belt where “sub-surface irrigation” is very likely to have a positive impact on rainfed fields. We assumed that water was non-limiting for those fields located in areas with presence of water table within the rootable soil depth during the growing season. At these 19 RWS, separate simulations were performed for water-limited (no influence of water table) and non-water limited environments (soils with water table within the rootable soil depth during the maize growing season) and results were weighted based on their relative share of maize harvested area. In the case of irrigated crops in the southern Great Plains (OK, TX and southeastern KS), maximum temperature during the peak of the growing season was reduced by 0.5ºC to account for the ‘cooling’ effect associated with frequent irrigations in this region. Finally, simulated Yp and Yw for northern locations at ND, SD, MN, and WI were relatively low and the resulting yield gap small (ca. 10% of simulated yield potential). We suspect that potential yields are higher than the current Hybrid-Maize model predicts, possible because the current trigger for a killing frost is too conservative.
Simulations utilized weather, soil, and management data obtained for each RWS. For each RWS, all selected soil types were simulated and then weighted by their relative proportion to retrieve an average Yw at the level of the RWS buffer zone. Quality control of results was performed following the guidelines provided by Grassini et al. (2015). A weighted average actual yield was calculated based on the actual yield reported, separately for rainfed and irrigated crops, for the counties that coincide with the buffer zone and the relative contribution of each county to the total crop harvested area in the buffer zone. In those states in central and eastern Corn Belt where actual yields are not disaggregated by water regime but irrigation may still be important in some specific areas (e.g. central WI, central-east IL, southern MI, and northern IN), counties with large irrigated area were not included for the calculation of rainfed actual yield based on irrigated harvested area maps (http://www.agcensus.usda.gov/Publications/2012/Online_Resources/Ag_Atlas_Maps/Crops_and_Plants/). There were, at least, 5 counties within each RWS buffer (average of 10 counties per RWS). Reported Yw and Yp in the Global Yield Gap Atlas are long-term (20+ years) averages.
Yield gap (Yg) was calculated as the difference between long-term average Yw or Yp and average (2005-2014) actual farmers' yields. Including more years before 2005 in the calculation of average actual yield would bias the estimate of average actual yield due to a strong, positive technology trend in the USA. In a few years (2005 and 2012), a severe drought affected summer crops and an important fraction of the planted maize area was not harvested in the western part of the Corn Belt. Hence, the actual maize grain yield reported for those years represents the yield from the most favorable environments for maize production within each RWS buffer. To correct this bias, we adjusted the actual maize yields based on the proportion of planted area that was not harvested within each RWS buffer.
Management practices were obtained for each RWS buffer zone. In the Corn Belt, sowing date, cultivar maturity group, and seeding rate were obtained from a large producer dataset including management data from more than 8,000 fields sown with soybean during the 2014-2017 cropping seasons (Rattalino Edreira et al., 2017). Late sowing date is a major cause for soybean yield gap in the US North Central region; hence, we derived the sowing date for our simulations from the 5th percentile of the sowing date distribution in each buffer, which typically corresponded to late-April and early-May sowing. Using average sowing date would have led to an underestimation of the yield potential and yield gap. For irrigated soybean in the state of Arkansas, we used the recommended sowing date and cultivar maturity group to maximize the yield potential for full-season irrigated systems (Salmerón et al., 2016). In the Mississippi river valley, we excluded double cropping system as it represents < 15% of the irrigated soybean harvested area (USDA NASS, 2004-2008 period).
Simulations using maturity of the most widely grown maturity group for the region surrounding each RWS were performed using APSIM soybean (v7.9) model (Holzworth et al., 2014). The model was previously validated for its ability to simulate soybean yield potential across a wide range of environments in the U.S. Corn Belt (Archontoulis et al., 2014, 2020, Ebrahimi-Mollabashi et al., 2019, Martinez-Feria et al., 2018) and found to be robust at portraying key G x E x M interactions across a wide range of yields, from 1.5 to 6.5 Mg ha-1. The model has a set of generic maturity groups (from MG 00 to MG 9, increments every 0.5 group) similarly to hybrid-maize model, which means minimum input requirements by the user. For details on the generic cultivars we refer to Archontoulis et al., (2014). We set up APSIM soybean to simulate a water-limited production situation. We used the SoilWat water balance model (typing bucket, Prober et al., 1998). Crop roots allowed to grow up to 1.5 m, which is the average max soy depth in the central US Corn Belt (Ordonez et al., 2018; Nichols et al., 2019). Soil water hydrological parameters developed by using texture class, plant available water, and Saxton and Rawls (2006) pedotransfer equations. To account for differences in initial soil water at planting time among years, simulations of rainfed crops were initiated on Jan 1 assuming 100% of plant available soil water. In APSIM, the soil water balance typically reaches equilibrium within 2-3 months. Previous crop residue on Jan 1 was assumed to be maize (amount 4 t dry matter /ha). The impact of water table on yields was accounted for similar as for the maize simulations. Briefly, we assumed that water was non-limiting for those fields located in areas with presence of water table within the rootable soil depth during the growing season. For the RWS with presence of water table, separate simulations were performed for water-limited (no influence of water table) and non-water limited environments (soils with water table within the rootable soil depth during the maize growing season) and results were weighted based on their relative share of maize harvested area.
Soybean yield potential was simulated for all the years for which weather data was available, assuming no limitations to crop growth by nutrients. For each RWS, all selected soil types were simulated and then weighted by their relative proportion to retrieve an average Yw at the level of the RWS buffer zone. A weighted average actual yield was calculated based on the actual yield reported, separately for rainfed and irrigated crops, for the counties that coincided with the buffer zone and the relative contribution of each county to the total crop harvested area in the buffer zone. There were, at least, 5 counties within each RWS buffer (average of 10 counties per RWS). Reported Yw and Yp in the Atlas are long-term (20+ years) averages.
Yield gap (Yg) was calculated as the difference between long-term average Yw or Yp and average (2009-2018) actual farmers' yields. Including more years before 2009 in the calculation of average actual yield would bias the estimate of average actual yield due to a strong, upward technology trend in the USA. Similar to maize, the Yp and Yw for some locations in the northern fringe of the region was relatively low and the resulting Yg small. We suspect that potential yields are higher than the current model predicts, possible because the current trigger for a leaf senescence as a result of cold damage is too conservative.
Management practices were obtained for each RWS buffer zone. Average sowing date was retrieved from extension bulletins, variety performance trials, and local agronomists. Requested information included: dominant crop rotations and proportion of each of them to the total harvested area, average sowing dates, actual and optimal plant population density. The provided data were subsequently corroborated by other national experts. Cultivars of winter wheat in the Great Plains, winter wheat in Ohio and spring wheat in the norther great plains have respectively 82.25, 88.25, 80.17 biological days from harvest to maturity with a photoperiod sensitive coefficient of 0.00263, 0.00263 and 0.001467.
Simulations using maturity of the most widely used cultivar for the region surrounding each RWS were performed using SSM Wheat (Soltani and Sinclair, 2012). The model was previously validated for its ability to simulate hard red winter wheat phenology and yield potential across a wide range of environments in the US southern Great Plains (Lollato et al., 2017; 2019) and found to be robust at portraying key G x E x M interactions across a wide range of yields derived from 45 environments, ranging from 1.5 to 8.5 Mg ha-1. The calibration and validation of the SSM Wheat model for phenology and yield potential of other wheat types in different regions (i.e., hard red spring wheat in the US northern Great Plains, and soft red winter wheat in eastern US) occurred against data from intensively managed wheat trials (Shawn Conley, personal communication; Quinn and Steinke, 2019) and variety performance tests. For hard red spring wheat, the yield range in the 21 site-years validation dataset was 1.32-7.33 Mg ha-1, and for soft red winter wheat it was 2.76-12.1 Mg ha-1 across 23 site-years. Model validation indicated an overall a root mean square error below 5% for phenology and below 20% for grain yield.
We set up SSM Wheat to simulate a water-limited production situation. Crop roots were allowed to grow up to 1.5 m, which is the average max wheat depth in the central US Great Plains (Awad et al. 2018). Soil water hydrological parameters were derived from Saxton and Rawls (2006) pedotransfer equations. To account for differences in initial soil water at planting time among years, either the growth and development of the previous crop (i.e., wheat, corn, or soybeans) was simulated and the soil water content at crop maturity was used as initial soil water content for the wheat crop; or the soil water dynamics during the preceding fallow period (~15-d when following corn, ~3-m when following wheat, or 14-month duration) was simulated. In both cases, the SSM model was used for simulating the water balance.
Wheat yield potential was simulated for all the years for which weather data were available, assuming no limitations to crop growth by nutrients. For each RWS, all selected soil types were simulated and then weighted by their relative proportion to retrieve an average Yw at the level of the RWS buffer zone. Spring wheat and winter wheat were simulated separately for two stations in Montana, which included both type of wheat, and their results were weighted in each buffer using the harvest area proportion of spring over winter wheat (USDA CDL 2017). Similarly, a weighted average actual yield was calculated based on the actual yield reported (separately for spring and winter wheat) for the counties that coincided with the buffer zone and the relative contribution of each county to the total crop harvested area in the buffer zone. There were, at least, 5 counties within each RWS buffer (average of 10 counties per RWS). Reported Yw and Yp in the Atlas are long-term (20+ years) averages. Yield gap (Yg) was calculated as the difference between long-term average Yw or Yp and average (2009-2018) actual farmers' yields.
Yield potential was estimated by simulation using the ORYZA (v3) crop model (Bouman et al., 2001). This model was chosen due to its widespread use and existing body of work validating it for various rice cropping systems. Further calibration and validation of this model was required to adequately simulate rice yield potential for representative high-yielding varieties typical of the types most widely planted in major U.S. rice-producing regions as described in Espe et al. (2016). In order to minimize the effect of variation between simulations, yield potential was simulated for each buffer zone over a 15-year time span at all locations except those in LA, which only had 13 years of weather data. Long-term mean yield potential in RWS buffer zones and as aggregated for larger spatial scales followed GYGA procedures.
For each buffer zone, the average emergence date as reported by state agronomists was used to initiate simulations. Sensitivity analyses were performed to evaluate the impact of using the long-term average emergence date rather than a distribution of emergence dates centered at the average, with only slight yield differences observed (absolute difference of less than 0.25 Mg ha-1; results not presented). Therefore, the average emergence date was deemed suitable for simulating yield potential. Annual simulated yield potentials were then averaged by buffer zone to determine the buffer zone yield potential. Individual simulation results were quality controlled for unrealistic results or failed simulations prior to averaging.
Data from the USDA-NASS database (USDA - National Agricultural Statistics Service, 2016) were used to determine actual yields within each buffer zone. Since buffer zones were constructed without regard for state or county boundaries, county-level data were retrieved and aggregated to obtain estimates for each buffer zone. In order to do this, the buffer zone average yield was calculated as a weighted average of county estimates, where weights were determined by the proportion of buffer zone harvested area within each county.
Where Yk is the average yield for buffer zone k, µj is the average reported yield for county j, n is the number of counties with harvested acres in buffer zone k, aj is the harvested area of county j in buffer zone k, and ak is the total harvested area in buffer zone k. To minimize potential confounding effects of yield trends over time, only the most recent reported data (2010 to 2014) was used. Buffer zone estimates were calculated by year and then averaged across years to get the average buffer zone yield.
† We thank Dennis Todey (South Dakota State University), Ken Scheeringa (Purdue University), Rick Wayne (University of Wisconsin-Madison), Mark Seeley (University of Minnesota), Jenny Atkins (WARM Program, University of Illinois at Urbana-Champaign), Daryl Herzmann (Iowa State University), and Bill Sorensen and Natalie Umphlett (UNL) for their help to access historical daily weather data.
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Data from the Global Yield Gap Atlas is available for commercial use. We have different commercial license types available, either for a single use of the data within a project context or multiple use and commercialization, suiting your needs. Please email Patricio Grassini (UNL) or Martin van Ittersum (WUR) to discuss options.
Bruce A. Linquist
Dept. of Plant Sciences, University of California - Davis, Davis, CA, USA
Matthew B. Espe
Dept. of Plant Sciences, University of California - Davis, Davis, CA, USA
LSU AgCenter, College of Agriculture, Louisiana State University, Baton Rouge, LA, USA
LSU AgCenter, College of Agriculture, Louisiana State University, Baton Rouge, LA, USA
Rice Experiment Station, California Cooperative Rice Research Foundation, Biggs, CA, USA
Net-Profit Crop Consultancy PLLC, AR, USA
Dept. of Agriculture, Southeast Missouri State University, Malden, MO, USA
University of California Cooperative Extension, Oroville, CA, USA
Texas A&M AgriLife Research Center, Beaumont, TX, USA