PRECISION AGRICULTURE INITIATIVE FOR TEXAS HIGH PLAINS

2001 ANNUAL COMPREHENSIVE REPORT

Texas Agricultural Experiment Station and Texas Agricultural Extension Service

Texas A&M University System

 

Principal Investigator:           Robert J. Lascano (r-lascano@tamu.edu)

                                                Texas A&M University – USDA-ARS

                                                3810 4th Street

                                                Lubbock, TX 79415

 

                                    Name                           Title/Agency                            Location

Cooperators:              Jill Booker                    Res. Assoc., TAES                  Lubbock

                                    Kevin Bronson Asst. Prof., TAES                    Lubbock

                                    Ted Wilson                   Prof. and Res. Direc.,               Beaumont

                                    Jim Bordovsky Res. Eng.                                  Halfway

 

Project Title:  The Balance and Variability of Water/Nitrogen within Large Agricultural Fields.

 

Primary Research Location: Lamesa and Helms Farm, TX

 

Project Objectives:

 

Objective 1:    Quantify the spatial and temporal variability of factors that can be addressed by precision agriculture practices.

 

Objective 2:    Develop and evaluate instrumentation and software to measure and analyze variability in crop production and plant response to that variability.

 

Objective 3: Evaluate the application of variable rate irrigation to cotton.

 

 

Reporting Period:      1 January 2001 — 31 December 2001

 

A.     Summary of Progress (Address all applicable objectives; data must be included)

 

Objective 1:    Quantify the spatial and temporal variability of factors that can be addressed by precision agriculture practices.

 

Lint Yield as a Function of Variability of Soil Factors in a Large Field. Field heterogeneity may affect yield potential, irrigation responses, and N transport. A water and N balance study was conducted in a large cotton field beginning in the spring 1998 to determine lint yield and N uptake potential related to local water and N input. Two irrigation levels, 50% ET and 75% ET, were applied from north to south across the field. In 1998, lint yields increased significantly with increasing irrigation (P > 0.0012). There was neither an effect of N inputs nor interaction between water and N inputs (P > 0.6780). However, the covariance of the model was significant on lint yield and N uptake (P > 0.0001). Therefore, a state-space approach was used to identify the spatial soil variability along transects. Lint yield, soil water, P2O5 content, and elevation were correlated in space. The state-space equations were determined through multivariate autoregressive processes to quantify the spatially correlated parameters that create spatial difference in a heterogeneous soil. Results showed that the natural landscape variability could affect lint yield and N uptake potential related to water and N use. Furthermore, the variability of our field measurements can be described with state-space models. These results are summarized in the publications listed below.

 

Objective 2:    Develop and evaluate instrumentation and software to measure and analyze variability in crop production and plant response to that variability.

 

Multispectral Remote Sensing Related to Water and Nitrogen Use in Irrigated Cotton. Assessment of real–time crop and soil conditions using remotely sensed data promises to realize site-specific water and N application in large fields under semiarid conditions. Plant/soil reflectance and spectral vegetation index have been used in characterizing soil, water, nutrient, and plant development conditions, in forecasting crop yield, and in making day-to-day farm management decisions in irrigation and fertilization. The objectives of this study were (i) measurement of cotton/soil reflectance related to specific irrigation and N fertilization, (ii) determination of cotton/soil spectral and agronomic characteristics, (iii) assessment of variability in N status and lint yield across large cotton field, and (iv) to forecast irrigation and N fertilization using spectral vegetation index. These results are summarized in the publications listed below.

 

Objective 3:

            Evaluate the application of variable rate irrigation to cotton.

 

Summary. The performance of a variable rate irrigation system on a center pivot was evaluated during the 2001-growing season. This performance included two objectives: 1) evaluation of delivery rates and positioning, and 2) phenological responses of cotton irrigated with variable amounts of water. Both objectives were preliminary and the evaluation was done at the Texas Agricultural Experiment Station at the Helm’s Farm, near Halfway, TX. Our results only concentrate on objective 2, as the first objective is part of an ongoing project by Jim Bordovsky.

For the purpose of variable rate irrigation a land area under the pivot was divided into 3 crop management zones (CMZ), each receiving different quantities, i.e., variable, of water during the growing season. Irrigation applications were determined according to the potential moisture holding capacity of the soil, which varied spatially due to variability in soil texture and topography. These two parameters were determined by taking soil samples to measure texture and elevation measurements to determine slope. Texture and slope were selected based on past research showing the importance of these two factors in determining cotton lint yield across a field. Crop water requirements were based on the evapotranspiration (ET), calculated from a Penman-Monteith equation. Our criterion for irrigation was to apply less water to areas with soils with a higher water holding capacity, which received a lower application rate, i.e., 60% ET, than to areas with soils with a lower water holding capacity, which received a higher application rate, i.e., 100% ET. In our research, each CMZ was divided in 2 parts, one receiving a base rate of 80% ET, or a variable rate according to the pre-determined soil water holding capacity.

To evaluate the cotton phenological response to variable rate irrigation, soil and plant measurements were done during the growing season (July – September). Soil measurement consisted of measuring soil moisture profiles every two weeks using neutron attenuation at 64 locations. Plant samples were collected twice a month at the same 64 locations, measuring plant height, number of leaves, leaf area index (LAI), number of bolls/squares, plant fresh biomass and plant dry weight. Additionally, plant reflectance was measured using a portable multi-radiometer. The crop was hand-harvested (24 October 2001) at the 64 sampling locations.

We evaluated our preliminary results by comparing for each CMZ the base and variable rate. Soil water content showed an increase for areas with higher application rates compared to the same area with lower rates. Results from LAI, plant height and crop reflectance measurements showed that plants under similar conditions showed better development, i.e., higher measurements of LAI, height and plant biomass, for higher application rates than for lower. Results showed that VR leveled out differences in the field. Measured differences in plant height and crop reflectance for cotton in different sections under the base application rate were similar to those under variable rates. Fresh plant biomass and number of bolls per plant showed that cotton under variable rate application with 60% ET on clay soils was water stressed. Lint yield showed a gain for variable rate on the slope with 100% ET and a loss on clay with 60% ET when compared to lint with the 80% base application rate. Lint yields irrigated with the 80% ET base application rate were fairly constant throughout the field. Results are preliminary due to equipment installation delays the cotton crop was irrigated late into the growing season. These experiments will be repeated during the 2002-growing season.


 

Introduction. Lack of water during the growing season is the limiting factor in the production of agricultural crops on the Texas High Plains (THP). The semi-arid climate in combination with persistent high winds, results in a high water demand. As a result of the climatic conditions the THP heavily rely on the use of groundwater for the production of crops. Gardner et al. (1996) expressed it, “…irrigation is the basis for an economy and a way of life”. Because of good soils and irrigation, the THP region, alone, would rank very high in agricultural production as a separate state in the U.S. or as another country in the world (Howell and Musick, 1997). Water for irrigation is obtained from the non-replenishable underground Ogallala aquifer. Water has been withdrawn from the aquifer for many years and as a result of overdraft, the future of Texas agriculture is uncertain. The effects of overdraft are likely to be the most severe in the southern Great Plains, where significant irrigated area may be removed from production within the next 20 years (Vaux et al., 1996). Since approximately 95% of the water pumped from the Ogallala is for irrigation (McReynolds, 2001), the severe decline of the water table prompted for changes in water management strategies. One of the changes is the use of deficit irrigation. Crop water demand is determined from the evapotranspiration (ET), consisting of the evaporation of soil water and the transpiration of a crop, as calculated with a Penman-Monteith equation. While regular irrigation applies water according to the ET, deficit irrigation exposes plants to a certain level of water stress by applying less than the water demand.  Optimum crop yield can be obtained through allowing a certain level of yield reduction of a given crop while higher returns can be obtained with saved water, which can be diverted to irrigation of other areas (Kirda and Kander, 1998). Deficit irrigation is now widely practiced on the THP for cotton and literature regarding crop performance with various water treatments and crops is available (Lyle and Bordovsky, 1995; Bordovsky et al., 1992). Additionally, reducing irrigation water losses and increasing water use efficiencies requires a new approach towards irrigation technology: precision irrigation. Precision irrigation is a term given to irrigation methods that recognize and manage spatial and temporal variations in the soil-plant-atmosphere system. The objective of precision irrigation is to improve the control of water input, together with fertilizer and chemicals, to increase application efficiency and to reduce water use (Cook and Bramley, 1998).

The THP landscape is characterized by the presence of center pivot (CP) systems, which are considered an efficient means of irrigation. A center pivot is a moving irrigation system that rotates around a fixed point, a pivot (Broner, 1998). The application rate varies laterally because the CP lateral covers more area per unit length towards the outer end. Center pivots are classified according to pressure or nozzle type. High-pressure systems have a pressure of >3.5 kPa at the pivot; medium pressure systems work with pressures between 2.5 to 3.5 kPa, and low-pressure systems have < 2.5 kPa.

Originally, CP’s sprayed water under high pressures through the air. However, losses due to water evaporation and low uniformity resulted in low irrigation and application efficiencies. With the introduction of LEPA (Low Energy Precision Application), an irrigation system designed for maximizing irrigation efficiency and increasing rain utilization, a forward step towards significant savings in both water and energy requirements was made. LEPA is a self-moving circular or linear irrigation system that applies water for the production of crops and forage in an energy efficient manner. Water is distributed directly to the furrow at a very low pressure through drop tubes and orifice controlled emitters (Lyle and Bordovsky, 1980). Since water is not sprayed through the air by high pressures, water losses due to evaporation are significantly reduced. Additionally, the water is applied directly into the furrow, which leads to very high application efficiencies. Since the introduction of LEPA much research has been conducted on their efficiency. High application efficiencies from 95-98% for LEPA when compared to spray sprinkler methods were found, with negligible runoff or deep percolation (Schneider, 1999).

Present technology applies water uniformly throughout the field, even though the field may not be uniform. Although efficiency has improved due to LEPA, the spatial variability of the soil is not considered in the application of water (Kaspersma and Sonnemans, 2000).

A technology that is still in development and could potentially save more water is Variable Rate irrigation (VR). According to Bordovsky et al., 2000, areas within a field may require different quantities of irrigation due to variation in soil texture, depth of soil, and the effect of topography on rainfall runoff (lower elevations benefiting, or suffering, from runoff from higher elevations). Instead of treating entire fields uniformly, precision VR allows on-the-go adjustments in the rate of water delivery to specific portions of the field (Leidner, 2000). Non-uniform distribution of irrigation based on topography and water holding capacity of the soil profile could better utilize both rain and irrigation water and improve water use efficiencies. Although this does not necessarily mean water savings, re-allocation of the water may result in higher water use efficiencies and thus crop yield.  Another advantage is that crops could also benefit by changing irrigation amounts at points (along the pivot lateral) as the relationships among soil chemical properties, pest infestations, production inputs, and crop yields are determined (Bordovsky, 2000).

Research reports on variable rate application of irrigation water are available. Kincaid (1997) developed a sprinkler head with a pin that moves smoothly in and out of the nozzle that reduced the flow to about 35 % of a nozzle at full capacity. Another type of variable flow sprinkler head consists of a digitally controlled metering device (Camp et al., 2000). Other types of variable rate systems use multiple manifolds to vary the flow-rate, in which several individually controlled manifolds each delivering discrete but different flow rates, and each designed at a certain water volume that could be combined into a range of flow rates at the drop  (Bordovsky et al., 1992; Duke et al., 1992; Fraisse et al., 1992; Camp et al., 1998). Currently, most of this technology is not yet commercially available and their implementation is mainly restricted to research applications.

The two objectives of this research were to test and evaluate the functioning of a CP VR system designed by J.P. Bordovsky (a similar VR system on a linear move irrigation system was described in Bordovsky et al., 1992), and to find differences in crop phenological response between VR application, taking spatial variability in the field into account, and uniform water application, thus neglecting spatial variability in the field. However, in this report we will only discuss results from our second objective.

 

Material and Methods

 

Description of the Research Area

The research was conducted at the Texas Agricultural Experiment Station in Halfway at the Helms farm (long. 101° 57’, lat. 34° 11’), on the Texas High Plains (THP). Fig. 1 is a map of Texas showing annual precipitation and location of the experiment site in Halfway. The altitude of the research site is 1045 m above sea level. The semi-arid climate in this area is characterized by an average annual rain of 450 mm and an annual water evaporation of 2300 mm. For the production of crops, ground water is pumped from the Ogallala aquifer, and used for irrigation in almost 50% of the area under cultivation.

            The soil of the research area consists of an Olton Loam (fine, mixed, thermic Aridic Paleustolls), characterized by the presence of a caliche layer that on average is 1 m below the surface. Caliche is a layer of indurated material near the surface, more or less cemented by secondary carbonates of calcium and magnesium, precipitated from the soil solution. The presence of such a layer affects penetration of roots into the soil and the movement of soil water.

For this research, a cotton crop variety Paymaster 2200, planted on 24 May 2001, was irrigated with a standard ¼ mile Zimmatic™ center pivot equipped with a VR system. The CP consisted of 8 spans each 48.8 m in length, covering a field with a radius of almost 400 m and 47.8 ha. On the outer 3 spans, a VR system was mounted. Except for the research area, the field was irrigated with a deficit, receiving 80% ET of the crop, which was uniformly applied with regular LEPA. The center pivot received water from 3 wells, which at top capacity pumped 2.3 m3/min, sufficient to irrigate the crop at 80% ET.

The research area, 4.8 ha, covered a 60º angle over the outer 3 spans at the south side of the field (Fig. 2) and received water with the VR system. The south side of the field had a lower elevation than the north side and there existed some variation in soil texture. According to spatial variability in soil texture and topography, the field –as described in Determination of the Crop Management Zones- for our purpose was divided into 3 different crop management zones (CMZ), each representing areas of similar characteristics. Application rates in this area varied between 60-100% of the ET.

The main advantage of the VR system compared to a conventional one is that it allows irrigation according to local requirements in the field by changing flow rates over part of a CP span (Fig. 2), instead of uniform application of irrigation water over the field. Different application rates for the CMZ’s were programmed into the control system for the control program of the center pivot allowed flow-rate changes in the field over 3º increments. The minimum area allowing variation in the irrigation rate, consisted of the length of 1 manifold over a 3º angle of the circle, equaling about 250 m2, which is 0.025 ha.

The design of the VR system required water to be supplied from the pivot lateral through pressure regulators and solenoid valves to each of three manifolds comprising the manifold unit. Three manifold units were present per span. Hoses were used to direct water from the manifolds to the modified LEPA applicator. Initial nozzle sizes for each applicator provided rates of 1x, 2x, and 3x, which, in various combinations, which provided 6 discrete irrigation amounts ranging -with 20% increments- from 20% to 120% of a base irrigation rate. In total, the three spans were equipped with ninety-six specially constructed LEPA variable rate applicators (Bordovsky et al., 2000). To avoid large pressures variations in the main system, a pump at one of 3 wells is equipped with a pressure regulator to adjust and maintain the pressure at certain level at any delivered flow rate. In case of high flow rates, a booster pump is connected at the pivot to maintain system pressure. Before the water enters the manifolds and drops with pressure-designed nozzles, it passes pressure regulators to ensure the right pressure for the nozzles.

 

Data Collection

Data available for this research were collected during the summer of 2001, from May to October. In the first week of June, 64 aluminum neutron access tubes were installed pre-determined locations over 9 east west transects in the research area over the CP spans 6,7 and 8. Holes with a depth of 1.5 m were drilled using a Giddings Coring Drill.  Additionally, soil samples were collected at 33 locations. The location of each access tube was determined by using a GPS Sattloc SLX.

Data on field characteristics such as elevation and slope were collected for 64 locations by using a field level (Model 8114, David White Instruments, Menomonee Falls, WI, USA). The elevation data were plotted in a GIS using Arcview 3.2, and an overview of the elevation and slope of the research area was created. Soil samples were collected over 4 depths, 0.2 m each, at 33 locations throughout the field for determination of the soil texture in the research area. Samples were air-dried and sieved to 2 mm. Soil textures were determined in the laboratory using the hydrometer method (Gee and Bauder, 1986). Soil texture together with the elevation was used to determine the crop management zones.

From July to September, crop samples were collected every other week at the 64 neutron access tube locations in the research area. From the collected plants, plant height, number of leaves, leaf area index (LAI) were measured. Number of squares and bolls were counted, and fresh and dry weight of the plants and bolls were measured using a scale. During July and September, a crop scan (MSR5 Multispectral Radiometer, Cropscan Inc.) was used to measure crop reflectance, which is an indicator for green mass of the plants. In October, lint yield samples were collected by hand as an indicator of lint yield.

Soil moisture content was measured at the 64 neutron access tube locations every 10-14 days during July to September. Using a neutron probe (CPN Corporation, Model 503 Hydroprobe, Martinez, CA), soil moisture measurements were taken in 0.3 m increments to 1.5 m depth.

During the irrigation season, VR flow rates, pressures and positioning system were collected. Flow rates were measured using a hang scale, stopwatch and bucket. Pressures were measured with a pressure gauge. For this, small Schreader valves (comparable to valve-stem in car tubes that can be fixed into almost any pipe conduit) were located throughout the system to which the pressure gauge was connected. For the positioning system, stakes were placed at known positions in the field, which were determined using a tape measure (every 3º in the research area in a transect from west to east). Weather data of the season 2001 were obtained from the Texas Agricultural Experiment Station in Halfway, located 1 km south of our research plot.

 

A.                 Determination of the Crop Management Zones (CMZ)

 

The CMZ were assigned using soil texture and slope.

Soil Texture

Soil samples were collected at the neutron access tube locations, each 30 m apart, of the middle (east west) transect of the CP spans 6, 7 and 8. In total, 33 samples of each 4 layers with 0.2 m increments (0-0.2 m, 0.2-0.4 m etc.) were used for the determination of the soil texture. Because of time constraints before the irrigation with VR started, only the two top depths, i.e., 0-0.2 m and 0.2-0.4 m, were analyzed for soil texture. At a later time during the research, also of the 2 other depths, i.e., 0.4-0.6 and 0.6-0.8 m, soil textures were determined. Results of this soil analysis for clay content were plotted in a GIS map.

 


Slope

The slope of a field may affect the application efficiency of irrigation and rainfall due to potential runoff by which the water is lost for a specific location. With the development of LEPA, a technology to reduce runoff in the furrow by creating small dikes was introduced (Lyle and Bordovsky, 1981), which was also implemented in the research area. Despite diked furrows, runoff can occur due to erosion or overtopping of the dikes. Additionally, alternate furrows application was practiced ((Bordovsky et al., 1984) where runoff may take place in the intermediate ‘dry not-diked furrows’ in case of rain.

Elevation measurements were done using a level and rod and then used to determine the field’s slope. Elevation was measured at all 64 locations where neutron access tubes were situated at the top of the ridge and data were plotted in a GIS. Using the inverse distance weighing method (IDW), a map was created with elevation of the research area in reference to the center pivot (Fig. 3). Because runoff is not caused by the slope alone but also by the slope of the furrow, the slope between every two neighboring points in a row was calculated individually. Dividing the measured difference in elevation between points by the distance of the points in the row, furrow slope data were obtained. Finally, points with the same slope were connected with a line, creating a map with furrow slope contour lines in 5 categories, i.e., 1%, 0.8%, 0.6%, 0.4% and 0%. Division into these categories was done for the practical reason that these were the numbers retrieved from the calculations that could be connected easily.

 

Layout Crop Management Zones

The actual CMZ’s were determined according to their water holding capacity. Soils containing more clay have a higher potential water holding capacity than those with sand. The same applies for soils without a slope, which have a higher potential to use the applied irrigation water and rain, than sites with a slope that are susceptible to runoff.

Roughly, the research area could -according to soil texture- be divided into two zones, a clayey zone with a high water holding capacity, containing > 40% of clay and a sandy zone with a lower water holding capacity, containing < 40% clay. In the case of slope of the furrows, it was assumed that runoff occurs mainly when the slope >0.5%. Considering the map with furrow slope contour lines, the area within the 0.6% or more contour line was defined as sufficient slope for runoff. The area with <0.6% slope was considered less susceptible to runoff, having a higher potential to utilize irrigation water and rain. Reason for using the 0.6% contour line was instead of a 0.5% was that it was easily derived from slope calculations, while the 0.5% contour line was not.

The different CMZ’s were assigned to receive an application rate according to their potential water holding capacity, based on their potential ET as determined with the Penman-Monteith equation. One of the objectives of VR was to vary flow rates without an increase of the total water demand of the crop by reallocation of application rates. The base application rate in this field consists of 80% ET. Areas with high potential water holding capacity received less than this 80% ET base rate and areas with low potential water holding capacity received more than the base rate (BR).

Finally, three CMZ’s were distinguished:

1.      A clayey zone without slope, which was assigned to receive the lowest flow-rate of 60% ET,

2.      A sandy zone without slope, which was assigned to receive an intermediate flow-rate of 80% ET,

3.      A sandy zone with slope, which was assigned to receive the highest flow-rate of 100% ET.

To assure good monitoring of differences in crop phenological response and soil water content (SWC) between different water treatments, 32 out of 64 sample locations (neutron access tube locations) received the BR application and 32 received VR application. Of the 9 manifold units on 3 spans, 5 applied VR at 60%, 80% or 100% of the ET, depending on the location of the CP in the field. The 4 manifold units left, which was every other manifold, applied BR.

 

Crop Phenological Response

 

Methodology

 

B.                 Plant sampling

 

During July-September 2001, two weekly crop samples were taken. Six plants were cut at random at every of the 64 sample locations, shown in Fig. 3. Plant samples were processed in a laboratory. We measured plant height, number of leaves per plant, number of squares and bolls, plant fresh weight and dry weight, leaf area of the plants from which leaf area index (LAI) was calculated.

 

Plant Density

To determine the number of plants per m row for every sampling location, a plant count was done at the beginning of the growing season. At every sample location, 5 random plant counts were done by placing a 1 m rod along the row and counting of the plants within that m. Plant counts were average and this value was used for the calculations of LAI, fresh/dry weight of the crop and hand harvested cotton yield.

 

Leaf Area Index

The leaf area (LA) was measured using a LI-3100 Area Meter. The LAI was calculated as follows:

 

LAI = (plants per m2/ plants in sample) * (LA / area)

 

Where, LAI, is the leaf area index in m2/ m2; plants per m is the number of plants per m obtained from the plant count; plants in sample is the number of plants in sample (6 plants); LA is the leaf area measured with LI-3100; and Area is the area of 1 m row in m2. The rows were 0.76 m apart.

 

Fresh/Dry Weight

Fresh and dry weights of the 64 samples were measured every sampling date. Before the dry weight was measured, all samples were dried in an oven at a temperature of 75º C. Depending on the size of the bolls in the sample, the samples were dried for 2-3 days.  Fresh and dry weights are expressed in kg/ha, using the following formula:

 

Weight = (plants per meter/ plants in sample) * weight sample * 43.75

 

Where Weight is the fresh/dry crop weight in kg/ha; Plants per m, is the number of plants per m obtained from stem count; Plants in sample is the number of plants in sample (6 plants); Weight sample, is the fresh/dry weight of sample in g; and 43.75 is a conversion factor from weight in kg/m row to weight in kg/ha in m/m2.

 

C.                    Crop Reflectance

 

Additionally to plant samples, crop reflectance measurements were used as an indicator of crop development. Due to memory lost we were only able to collect data for 2 sampling dates. A crop scan measures the crop reflectance at a height of 2 m above the crop canopy, viewing a ground area of 1 m diameter. Spectral radiometer readings in millivolt were converted into spectral reflectance as percentage of reflectance. Center wavelengths measured were 460, 485, 500, 560, 600, 660, 700, 750, 800, 830, 880, 940, 1100, 1260, 1480 and 1650 nm.

            Different wavebands correlate with specific plant components. Li et al., 2000, found for example that near infrared reflectance (NIR) increased significantly with increasing irrigation, soil water content (SWC), plant fresh biomass (PFB) and plant N-content. One of the most significant relations between spectral and agronomic characteristics found by Li et al., 2000, was that NIR reflectance varied as a function of PFB and cotton lint yield was found to be related to the reflectance based normalized difference vegetation index (NDVI). The NDVI was determined as follows:

 

            NDVI =  (NIR – RED) / (NIR + RED)

 

Where NIR is the near infrared reflectance band between 797 and 829 nm, and RED is the red band between 648 and 674 nm

The NDIV and reflection of several wavelengths were plotted into a GIS to make differences in various CMZ’s the field visible. Additionally, reflections and NDVI were presented over a transect through the research area.

 

D.                Soil Moisture Content

 

For the measurement of the soil moisture content of the soil, a neutron probe was used. Since a neutron probe is not very sensitive to small differences in soil moisture, measurements were done every 10-14 d. The neutron probe measures moisture in the soil by use of a radioactive source and neutron detector. The probe is lowered into an access tube and neutron counts were obtained for five depths of each 30 cm (layer 1 = 0-30 cm, layer 2 = 30-60 cm etc.). In 1997, the neutron meter was calibrated, resulting in the following linear relation (Bordovsky, personal communication):

 

SW = ((CR503 * 7.10) + 0.43)/0.3

 

Where SW is the soil moisture content in m3/ m3; CR503 is the count in specific soil layer/standard count. The standard count consists of 10 readings on a neutral (not lowered into the soil) position.

 

E.                 Harvest Data

 

On 24 October 2001, cotton lint was hand harvested at all 64 sampling locations. At each location, two areas, each 0.76 x 5.33 m, equaling 1/2500 ha (30 inch rows x 17.5 ft = 1/1000 acre) were harvested. While harvesting, the number of plants in a sample and the number of bolls of the first 6 plants in the sample were counted and recorded to be able to combine these data with data previously collected in the research. The samples were ginned at the Texas Agricultural Experiment Station, where the total, seed and lint weight were measured. These data were then plotted into a GIS.

Additionally, lint yield was harvested with a cotton stripper. The yield monitor records the weight of harvested cotton (including burr and seed) every second together with the GPS position in the field. From the hand harvesting, a lint yield factor was derived indicating the ratio between total weight and lint weight. Data recorded with the yield monitor were multiplied with this factor and plotted into a GIS.

 

F.                 Mapping in Arcview

 

            Soil properties and plant development were mapped with Arcview, a geographical information system (GIS). In addition, information on elevation, soil (chemical) properties, soil water content, fresh and dry weight of plant matter, lint yield and NDVI’s, were also mapped using Arcview (v. 3.2), showing spatial variability of properties and characteristics in the research plots. Using the inverse distance weighted method (IDW), data collected at the 64 sample locations were interpolated, creating overview maps for the whole research area. The IDW option in Arcview interpolates data from the nearest neighbors and adds value to data from surrounding points by multiplying these with the inverse of the distance. The further a point, the smaller its weight in the interpolation. The number of neighbors was set at 6. The inverse power on the distance was set at 2. Although Arcview automatically determines map classifications, the number of classes was decreased to in most cases 5, and classifications were pragmatically reclassified into more equal and logic classes to assure a clear overview the maps created.

 

G.        Data Analysis over a Transect

 

A transect from the SE to NW corner of the research area was delineated and used for spatial analysis of the research data. The transect was defined from low to high elevation, crossing all 3 CMZ’s, by connecting the mentioned corners with a line between them, crossing the middle point of the research area. Every point (sample location) in the research area was connected perpendicular to the transect. Cross-sections were given a number in chronological order from southeast to northwest, starting with 1 and ending with 64. Our defined transect combined points and data from different locations, and offered the possibility to take a different look at the dataset. Data analysis along this transect proved reliable. Besides the transect, regression curves between various variables were analyzed. To find relations between different soil, water and lint yield properties, several variables were analyzed:

 


Results and Discussion

 

Crop Phenological Response

 

G.                Plant Sampling

 

Fresh Weight

            Graphs of VR and BR plant fresh biomass (PFB) are presented in Fig. 4. Our results show large variations in PFB for VR and rather constant and higher values for BR. Fresh weight in the clay zone is for VR almost overall the lowest and for BR overall the highest, indicating that crop growth in the clay zone is affected due to the reduced 60% flow rate. Variation in PFB for cotton between VR and BR on sand and slope are small.

 

Dry Weight

            Graphs of the plant dry weight (PDW), show the same trend as PFB, except for the fact that where curves of PFB decrease, the PDW increases. This is because bolls, which are about half of the total PDW, have a bulk density than leaves and stems. Overall, the dry biomass is 10-20% lower for VR than for BR cotton during the last sampling dates for which no direct explanation can be given.

 

Text Box: Table 1. Average plant heights during last 3 measurements.
	clay(m)	sand(m)	slope(m)
BR	0.64	0.61	0.59
VR	0.62	0.62	0.61

Plant Height

            Results show that most of the plant growth was established before implementation of variation of flow rates (day 213). Existing differences in plant height from before implementation of VR do not seem to in- or decrease later in the growing season. Plants on clay, sand and slope measure an average height over the last 3 measurements of in average 0.64, 0.61 and 0.59 m (Table 1). For VR, plants in the slope area (100%) are the only ones to show growth after implementation of varied flow rates, approaching the height of plants on sand and clay closely with an average over the last 3 measurements of 0.61 m and 0.62 m for both clay and sand. 

 

LAI

            The leaf areas of plants were measured to determine the LAI. The general dip that is recognized in all 3 charts is due to the change to a more random methodology of cutting plants. Decreasing LAI towards the end of the growing season is due to dying off of the cotton plant. Deviations of VR LAI from BR LAI are shown in Table 2.

The LAI’s showed clearly the pattern of water delivery over the field. For clay, a difference was measured in LAI from DOY 236 to 261. Cotton plants watered with the 60% VR application measured 7-13% lower LAI than those with 80% BR application. Additionally, LAI’s in the sand zone showed any difference, except for the first measurement at DOY 193. The measured difference, which varied between –5%-4%, can be considered negligible given the variation in measurements. In the slope section of the research area, the LAI from the start of the growing season had higher values for 100% VR than for 80% BR. With a highest measured difference in LAI of 25% halfway the growing season, slightly over a week after the actual variation in flow rates was started, VR LAI showed a steady deviation from BR of 10-16% over the last 3 samples.

 


Table. 2. Deviation LAI VR from BR.

DOY

dev.  clay

(%)

dev. sand

(%)

dev. slope (%)

143

0

0

0

193

4

12

9

207

6

3

4

221

4

-2

25

236

-7

4

16

248

-13

-5

10

261

-10

-5

15

 

Table 3. Deviation no. leaves on plant.

DOY

dev.  clay

(%)

dev. sand

(%)

dev. slope (%)

143

0

0

0

193

3

1

20

207

1

5

7

221

4

1

14

236

-15

1

6

248

-17

-1

-1

261

-23

16

5


Number of Leaves

            Except for clay, the number of leaves on plants did not show significant differences for the various application rates. In Table 3, deviations of VR to BR in number of leaves are presented. Data of clay shows 15-23% less leaves per plant for VR plants over the last 3 counts, marking a substantial difference. On sand, although the last count shows a deviation of 16%, any difference can be neglected since this one count stands too much on itself. Number of leaves per plant is in this area the same overall. Plants in the slope zone show substantial higher number of leaves for VR during the first 3-4 readings, but as the end of the season approaches, the difference becomes smaller (Note that the during count 1 and 2, water was still applied uniformly).  Nevertheless, 5 out of 6 counts are in gave a higher number of leaves for 100% VR, so it can be concluded that the crop in these rows overall contained a higher number of leaves per plant.

 

Text Box: Table 4. Deviation of VR to BR in number of bolls per plant.
DOY	dev.  clay	dev.  sand	dev.  slope
	(%)	no. bolls	(%)	no. bolls	(%)	no. bolls
248	-6	0.4	-2	0.1	3	-0.2
261	-11	0.8	10	-0.6	0	0.0
297	-15	0.9	4	-0.2	8	-0.4

Number of Bolls

During the first 4 plant samplings, bolls and squares were not counted separately. During counts 5-6, only bolls were counted, assuming that there was not enough time left for squares to develop into bolls before harvesting. Count 7 also consisted of bolls only, which were counted during hand harvesting of the cotton. In Table 4, deviations of VR and BR values are given for the number of bolls.

            The number of bolls showed the largest variations for clay. Plants with 80% BR had in average >10% more bolls than those with 60% VR. For sand as well slope counts varied but finally in both cases gave somewhat higher boll counts (about 5%) for VR. The development of fruit through the growing season shows variations in number of squares for the different flow rates. Considering the number of bolls, more variation exists between boll counts in BR sections than in VR rows. Plants in the BR clay area in average had 1 boll more than those in the sand or slope zones. With 60% VR, clay had about 1 boll less than with 80% BR application, diminishing the difference in boll counts between clay, sand and slope areas for VR application.

 

H.                Crop Scan

 

            Measured reflectance show variations of crop in the research area. Plotting the measured reflectance over the wavelength for the different VR and BR application rates, a pattern appears that especially expresses itself with large variations in wavelengths >1000 nm. Fig. 5, shows the reflectance for a crop scan reading on 19 August 2001. The figure for BR shows lowest reflectance for clay in higher wavelengths and higher reflectance for sand and slope. There higher wavelengths are often related to biomass, it is an unexpected pattern, since the slope area is considered to have the lowest water holding preference of all. Li et al (2000) however, derived a relation for MIR (1523-1752 nm) and plant water content (PWC) that describes the reflectance as a negative exponent of the PWC with the following function:

 

Ref% (MIR) =. 84.66 * PWC–0.1561

 

Applying this to the measurements, PWC of BR plants in the clay zone are higher than those in sand and slope area, respectively. This agrees with the pattern of water holding capacity according to which the crop management zones were divided. Reflectance in the higher wavelengths of VR plants shows no difference between clay, sand or slope, indicating that VR compensated the existing difference in PWC.

 

Text Box:

Text Box: Fig. 6. Red, NIR and MIR reflection over the transect.

 

 

Li et al (2000) also found a relation between plant fresh biomass (PFB) and the NIR band. VR as well as BR data show very little variation in reflectance in this area, indicating hardly any difference in PFB.

For short wavelengths, a difference in reflection occurs in the RED band (648-674 nm). Soil reflectance is discriminated in this band (Li et al., 2000). As explained in the methodology, RED and NIR bands can be combined into normalized difference vegetation index (NDVI). NDVI corresponds with the LAI of the crop. With hardly any noticeable variation in NIR reflection, a high RED corresponds with a low NDVI and vice versa. With the lowest RED reflectance for clay (see Table 5) it can be concluded from the graph that the LAI of clay for BR was higher than that of the sand and slope. The plants on the slope have the lowest NDVI for both application rates, indicating the lowest LAI overall.

            The graphs of reflectance of VR and BR show no difference from each other in any wavelength. Differences existing in one area are compensated by other areas, which means that VR showed neither increase nor decrease in crop development in this area when compared to BR.

            Three major wavebands (red, NIR and MIR) were plotted over the transect in the field. Fig. 6 shows that both RED and MIR bands’ reflectance decreased as you walked from east to west (1 to 64) along the transect. No direct difference is seen between VR and BR crop scan readings. The blue and the green band show slightly higher reflectance at the beginning than at the end. Although reflection for NIR is higher for the crop on sand than slope and clay, no direct relation was recognized.

Lower RED reflectance means lower soil reflection, which leads to the conclusion that towards the west in the transect, plant density or crop cover were higher than at the at the east side. It shows higher NDVI’s along the transect, which means higher LAI. While no difference can be noticed crop scan readings between BR and VR, the NDVI chart shows slightly higher NDVI’s for BR than for VR in the clay area (transect no. 45 and higher). NDVI plotted against site elevation shows higher NDVI’s for the higher sites.

  MIR reflectance showed a clear trend over the transect. This wavelength is related to the plant water content (PWC); higher reflectance is due to a lower PWC and vice versa. Overall, Fig. 6 shows higher reflectance at the low transect than at the high, indicating higher PWC in the upper transect. Taking a closer look, a difference is noticed for this wavelength between VR and BR reflectance. In the low transect, BR measurements show higher reflectance than VR. The mid section readings are scattered, but in the high region of the transect VR reflectance is in average higher than that of BR. Shortly said, plants in the slope zone contain higher PWC for 100% VR than for 80% BR and in the clay zone, this is the opposite for 80% BR and 60% VR application. Table 4.6 shows how MIR reflections vary between 20.9-21.6% for VR and 19.5-23.7% for BR application. Differences in PWC due to variation in the landscape and soil properties in the research area were corrected for by VR application.

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

I.                   Soil Moisture

            Average SWC’s measured during application of different flow rates are shown in Fig. 7. The SWC’s vary per soil, but seem to follow the application rates. Clay for example measured a lower average SWC in the first layer, but in deeper layers, BR 80% exceeded the SWC of VR 60%. SWC’s in the slope area show steady higher readings for 100% VR, which in average were 2.3% higher than those for 80% BR. Sand shows some variation in the first layer, but in deeper layers the soil moisture was about the same.

All curves show an increase for SWC below 1.2 m, where root water uptake by plants is minimal. Although it is assumed that the crop used all applied water and that no deep percolation took place, SWC for the highest flow rates of the slope and clay do show higher readings in the layer 5 than for the lower application rates.

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

J.                  Transect Data

 

Elevation and Slope

Measurements regarding elevation of the field were done in relation to the center pivot apron. The elevation varied over a height of 2.34 m from –1.65 m in the southeast corner of the field, to 0.69 m in the Midwest part. Fig. 8 (A) shows an increase for elevation along the transect in the slope zone from –1.65 – 0.1 m. Sand zone is characterized by an elevation of 0.1 – 0.5 m. Points in the clay zone were all located higher than 0.5 m. Slope data, Fig 8 (B), show steeper slopes for locations with low elevations. In the clay CMZ (transect No. 45 and up), hardly any slope existed.

 

Clay, Sand and Silt Content

            Fig. 8 (C) shows soil properties for an average of 4 layers over the first 0.8 m (0-2 m, 0.2-0.4 m etc.). Variation existed in clay, sand and silt content along the transect. The clay content showed an increase from east to west, from 34% in the low transect to 49% in the high transect. The area within transect No. 45 and larger was, containing >40% clay, was the clay CMZ. Sand content showed an inverse relation of clay along the transect. Silt content of the soil increased slightly as the clay content increased. Areas with low clay content also contained low silt.

 

SWC

Fig. 8 (D) shows the effect of VR on the SWC. Except for some points in the slope zone, the SWC for 80% BR in the slope and sand zone varies from 34 to 37%. The points showing higher SWC in the slope zone contained some more clay. For 8 out of 10 points in the clay zone, the SWC is between 38% and 43%. VR data show clearly different results for the SWC in the slope zone. The average SWC for VR is 39.4% with a minimum of 37.7 versus an average of 36.9 for BR application. Average soil moistures in the sandy zone are about the same for VR and BR, differing +0.5% for VR with 36.5%. Measured SWC in the clay zone are 39.6% for both application methods.

 


Lint Yield

            Lint yield over the transect, Fig. 8 (E), shows the effect of different water application rates in the field. Except for the first few readings, BR lint yield shows little variation with a mean of about 1150 kg/ha. VR lint yields follow the pattern of the 100-80-60% ET variation in application rates. Lint yield in the slope zone is in average 6.7% higher than with BR. In both the sand and clay zone, yields are lower than for BR with in the sand zone more scattered yields, but in the clay zone showing clearly lower values than for BR. 

 

SWC over Elevation

            The graph in Fig. 9 (B) clearly shows higher SWC for VR in the low elevations than for BR. Taking a closer look at the SWC for BR, no direct relation between SWC and elevation was derived from the graph. SWC in the sand zone (0.1-0.5 m) hardly vary, but the clay area (>0.5 m) shows great variation.

 

Lint yield over Elevation

            Lint yield in low elevations, Fig. 9 (C), show higher yields for VR than for BR. Yields in the area with an elevation of >0.5 m, which is mainly the clay area, picture a lower average lint yield for VR and rather constant, less scattered lint yields for BR.

 

SWC over Slope

            Results over the slope show similar results as those over the elevation. The graph of SWC over slope in the field shows a correction in SWC with for the higher slopes (>0.6%). The area with moderate slope (0.4-0.6%) is located in the sand zone. Uniform water application shows no clear variation in SWC. Although different flow rates were applied in the area without slope (0-0.2%), no clear differences in SWC content are visible in this area.

 

Lint Yield over Slope

For steeper slopes, lint yield shows some higher values for VR than for BR, while in the area with slope <0.6%, VR yields are overall lower.

 


SWC versus Clay Content

            Fig. 10 shows a larger selection of BR data than VR data for the reason that of the 33 soil sampling locations, only 11 were located in a VR row.

 

            The graph in Fig. 10 shows for BR a clear relation between SWC and clay content in the texture. Where the clay content ranges from 32.4 - 48.6%, SWC follows the trend from 34.2 – 42.3%. Measurements of VR SWC show more scattered results. In the lower clay ranges, the SWC is in average higher and in richer clay soil lower than compared to BR values.

 

SWC versus Sand Content

            Plotting the SWC versus the sand content of the soil, the inverse relation of SWC versus clay becomes visible. High SWC’s for low sand content and vice versa for higher sand contents for BR application. Although measurements of VR SWC are more scattered, the presence of more sand in the texture is partly compensated by the variation of flow rates over different areas.

                                                                       

Lint Yield versus SWC

            One thing that can be explained from Fig. 11 is that VR in average resulted in higher SWC than BR. Of the 10 lint yields at the lowest SWC, 2 are VR yields, while of the 13 SWC >40%, 4 were BR values. Measured lint yields were somewhat higher at increasing SWC. Although differences are small, the data show a rising trend from which can be carefully concluded that relation exists between SWC and lint yield.

 

Lint Yield versus Clay Content

No relation can be derived from the figure between clay content of the soil and lint yield.

 

Lint Yield versus Nitrate Content of Soil

            Although the higher nitrate contents (> 4 ppm) seem to show higher yields, points are too scattered out to draw any conclusions from this.

 

K.                Lint Yield

 

Average yields are presented in Table YY. Of main interest in the dataset is the amount of lint yield. The column “VR-BR lint” present the deviations of lint yield from VR and BR sections. The lint/water ratio was calculated by dividing the lint yield (kg) by the amount of water that was applied by the VR system (mm). It is used as an indicator of the water use efficiency; a higher lint/water ratio means more lint yield per amount of water applied.


Table 7. Average yields in different crop management zones.

 

lint

(kg/ha)

no. bolls

per 6 plants

no. plants in sample

SD lint

(%)

VR - BR lint

(% & kg)

VR application

(mm)

lint/water

ratio

VR clay 60%

1083

31.3

47.0

10.4

-5.5

98

11.0

BR clay 80%

1146

36.7

47.4

5.0

-62

131

8.8

VR sand 80%

1092

33.7

44.6

7.9

-6.9

131

8.3

BR sand 80%

1172

32.2

48.3

3.9

-80

131

9.0

VR slope 100%

1175

33.9

45.8

9.0

6.7

164

7.2

BR slope 80%

1102

31.4

44.2

6.2

74

131

8.4

 

Data show an unexpected difference of 7% between lint yield in the sandy CMZ. Why the sand data show different results, remains unexplained. Although this area was uniformly irrigated, the difference of 80 kg/ha is larger than anywhere else where yield was measured. In the other two CMZ, the VR lint yield shows a correlation between that of different delivery rates in comparison to lint yield with uniform application (80%). In the clay zone, a loss of 5.5% is measured at the 60% ET application. Lint yield in the slope zone shows a gain of 6.7% for the 100% ET application rate.

            From the variation in standard deviation (SD) we can conclude that lint yield from VR varied more than that from BR areas. The maps show lint yield for BR and VR application, created with data from the two irrigation treatments separately and thus suggesting what the research area would look like in case of the same treatment throughout the area. A large part of the clay zone, receiving 60% ET, has a lighter color than on the map of BR lint, indicating lower yields. Comparing the slope zone under VR with that under BR application, it can be noticed that this area overall has a darker color that in the previous case, meaning higher yields. Taking a look at the map as a whole, the water application pattern can be recognized with lower lint yield for the lower application rates and higher for 100% ET in the slope zone.

The number of bolls on the first 6 plants in the sample followed the pattern of division of flow rates in the research areas; more bolls per plant for crop with high water application rates than for low water application rates in the same CMZ. VR 60% on clay shows in average a loss of 4.4 bolls/6 plants in comparison to 80% BR plants. For sand, the difference of 1.5 bolls is negligible. In the slope area, 100% VR on average had 2.5 bolls/6 plants more than 80% BR plants, indicating a higher yield potential for VR plants. Variation in numbers of plants in different areas cannot directly be related to the application method, since variations in flow rates were only applied after plant emergence.

The lint/water ratios show hardly any deviations for cotton under BR. What can be noticed is the high ratio for 60% ET on clay and low ratio for 100% ET in the slope area. Although 60% clay showed the lowest lint yield, the water use in this section was most efficient of all CMZ’s. It can be concluded that plants in this area performed very well at the irrigation deficit of 60% ET. Because lint over the different CMZ’s showed no major differences, the lint/water ratio shows a relative inefficient water use for the 100% application on the slope.

 


Table 8. Average yields per application method.

 

lint

(kg/ha)

no. bolls

per 6 plants

no. plants in sample

SD lint

 (%)

VR - BR lint

(% & kg)

VR application

(mm)

lint/water

ratio

VR overall

1117

32.9

45.8

9.7

-2.1 %

131

8.9

BR overall

1142

33.4

46.7

5.5

-24 kg

131

8.7

 

In the end, a farmer is interested in the total yield of a field (or application method). Table 8, shows average overall yield from VR and BR sections. According to the table, overall lint yield in kg/ha is with 2.4% slightly lower for VR than for BR. Data from the sand area may be subscribed to be the factor diminishing the difference between overall VR and BR lint yields. However, eliminating the influence of the sand data and taking a look at the average lint yields in Table 7 (leaving both sand yields out of consideration), the overall lint yield for VR is 1129 kg/ha versus 1124 kg/ha for BR and thus not noteworthy higher (0.5 %). The average lint yield from sand VR and sand BR is 1132 kg/ha.

            Because VR application was based on re-allocation of irrigation water, the overall amount of irrigation water applied was the same for VR as BR. Since overall lint yields are the same, the lint/water ratios of the different treatments also show hardly any difference. Less efficient water use with 100% slope was compensated for by the 60% clay; VR application did not show a more efficient use of irrigation water than BR application.

 

Conclusions and Recommendations

 

L.                 Conclusions

The second objective of this research consisted of the evaluation of VR irrigation by measuring differences in crop phenological response between uniform and non-uniform applied irrigation water. The hypothesis was defined as follows: VR applies water according to the specific water requirement of the crop management zone; therefore a positive relation, i.e., better developed plants and higher lint yield per area, can be found in crop development and yield in a transect irrigated with variable rate application as compared to a transect in which water is uniformly applied with a fixed rate application.” During the research, it became clear that application of VR to the various crop management zones expressed itself in a difference in SWC, plant development and lint yield. SWC increased for areas with higher application rates compared to the same area with lower flow rates. Measurements on clay and slope showed this phenomenon, while SWC on sand confirmed uniform application. Overall, plants under similar conditions showed better development for higher application rates than for lower. LAI, for example, showed better development; higher values per measurement for crop under higher application rates as compared to that with lower flow rates under the same conditions. Various data showed that VR leveled out differences in the field. Plant height hardly varied for VR but under BR the plant heights varied according to the size of the application rate. Variations in measured crop reflectance over all wavelengths, which existed for plants in different sections under BR, were hardly visible for plants under VR. Also NDVI’s and MIR displayed a decreased variation between the different zones for VR than for BR. 

            However, where plants under high application rates on the slope gained in development, those on clay under low flow rates lost. Our results show that plants under 60% ET on clay suffered from a water deficit. Fresh plant biomass and dry weight showed, except for clay 60%, hardly any variation over different areas. Crop on clay applied with 60% ET stayed considerably behind on other crop. Number of leaves showed relative decrease for plants on clay irrigated with only 60% ET, but hardly any differences for sand or slope. The number of bolls per plant showed the same. Where plants on sand and slope showed some variation in quantity of fruit, plant on clay gave overall lower counts for 60% than 80%. 

Finally, the farmer is most interested in lint yield. Lint yield over the transect shows a gain for VR lint on the slope and a loss on clay. BR lint yield were fairly constant over the transect. Lint yield data from VR and BR overall show no increase for VR. The stated hypothesis was therefore incorrect. Although a positive relation, i.e., better developed plants, was found for areas with higher flow rates, no improved crop development and higher lint yield were measured in a transect irrigated with variable rate application as compared to a transect in which water is uniformly applied with fixed rate application.

 

M.              Recommendations

            Several recommendations regarding future research on VR irrigation can be made. In this research, VR was tested on cotton, over part of the growing season. Regarding the crop it must be noted that cotton is a crop that acts and reacts differently to its environment than for example corn, because it is a perennial crop. Although it is grown as an annual crop, plant systems operate in another mode. It is known that cotton shows great capability of adjusting to its environment, thus diminishing important indicators as water stress, LAI or lint yield. 

Secondly, the timing when variable rate application is started could be changed. Due to a heavy storm in April 2001, the center pivot with VR system was damaged as such that it needed to be replaced, with 2 months of delay for VR application as a result. Despite the fact that plant water uptake in the first month is a fraction of that when plants are mature, differences in plant growth between application rates may become more visible by starting VR application early in the season.

A third recommendation consists of the selection of the research area. One of the criteria of the crop management zones was slope in the field. The research site in this case was relatively small with some elevation differences. A larger research area with a more variation in elevation (and slope) it recommended. More spatial variability in soil properties and topography for a larger scale evaluation of VR application would definitely give more insight in the validity of this technology for increase in crop yields. 

 

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Schneider, A.D., 1999. ‘Efficiency and Uniformity of the LEPA and Spray Sprinkler Methods: A Review’. Transactions of the ASAE, 2000, Vol. 43 (4). p937-944

Senninger Irr. Inc. Orlando, FL, USA. Flow rate equation nozzle package.

Vaux, H.J., Jr., R.M. Adams, H.W. Ayer, J.R. Hamiliton, R.E. Howitt, R. Lacewell, R. Supalla, and N. Whittlesey, 1996. In Howell, T. and J. Musick, 1997. ‘Texas High Plains Irrigation…’, Internet: Wetting Front. Vol. 1, No. 1. USDA-ARS , Bushland, Texas, USA

 

B.     Education/technology transfer

 

·        Held a workshop titled “State-Space Analysis and Other Statistics and its Application to Precision Agriculture” at the Lubbock USDA-ARS center, 9 – 10 July, 2001. Dr. D. R. Nielsen and Dr. Ole Wendroth instructed the workshop. R. J. Lascano organized the workshop.

 

C.     Milestones Achieved:

 

·        During the 1998 and 1999 growing seasons, lint yield did not respond to nitrogen fertilizer due to the high content of residual nitrate–nitrogen in the soil. This indicates that the current recommendation of only sampling the surface 6 inches for soil nutrient management is erroneous and can lead to over fertilization.

 

·        Results from both growing seasons indicate that it is possible to estimate plant leaf area and plant biomass from plant reflectance measurements. The reflectance measurements are made with a hand-held radiometer.

 

·        Our state–space analysis indicates that it is possible to use this approach to identify management units in a field. Results indicate that we can explain lint yield variability with a 95% confidence using state-space analysis. This analysis shows that in Lamesa lint yield variability is related to irrigation amount, elevation and soil P2O5 content. These results are significant because they indicate that lint yield for a given location can be maximized using the state-space equations. For example, irrigation water in combination with P fertilizer can be variably applied on the field to maximize lint yield. Also noteworthy, is that in Lamesa NO3 content in the soil is not related to yield due to its very high concentration.

 

  1. Publications:

 

·        Lascano, R.J. and H. Li. 2001. Precision farming to improve water use Encyclopedia of Water Science (In press).

 

·        Lascano, R.J. 2001. Precision Farming and Nutrient Management. Encyclopedia of Soil Science (In press).

 

·        Li, H., R.J. Lascano, E.M. Barnes, Jill Booker, L. T. Wilson, K.F. Bronson, and E. Segarra. 2001. Multispectral reflectance of cotton related to plant growth, soil water and texture, and site elevation. Agron. J. 93:1327—1337.

 

·        Li. H., R.J. Lascano, J. Booker, L. T. Wilson, and K.F. Bronson. 2001. Cotton lint yield variability in a heterogeneous soil at a landscape scale. Soil Tillage Res. 58:245—248.

 

·        Li, H., R.J. Lascano, E. Barnes, J. Booker, L.T. Wilson, E. Segarra, and K. F. Bronson. 2001. Temporal patterns of cotton reflectance and NDVI-days lint yield modeling. p. 590—594. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN.

 

·        Li, Hong, R. J. Lascano, Jill Booker, L. Ted Wilson, Kevin F. Bronson, and Eduardo Segarra. 2001. State-space description of underlying field heterogeneity on water and nitrogen use in cotton. Soil. Sci. Soc. Am. J. (In press).

 

·        Li, Hong, R.J. Lascano, L. T. Wilson, and E. Segarra. 2001. Semivariance and cross-correlation of sand, water, cotton canopy temperature, and plant reflectance in the landscape. In: Third European Conference on Precision Agriculture, 18—20 June 2001, Montpellier, France, p. 241—246.

 

·        Yu, Man, Eduardo Segarra, Susan Watson, Hong Li and R.J. Lascano. 2001. Precision farming practices in irrigated cotton production in the Texas High Plains. p. 201—208. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN.

 

·        Chua, T.T., K.F. Bronson, R.J. Lascano, J.W. Keeling, A.R. Mosier, J.P. Bordovsky, C.J. Green, and J.B. Booker. Abstract. p. 588—588. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN.

 

·        K.F. Bronson, J.W. Keeling, T. Wheeler, R.J. Lascano, P. Dotray, A. Brashears, S. Searcy, K. Siders, J.D. Booker, Jill Booker, R.K. Boman, Hong Li, and T. Chua. 2001. On-farm testing of site-specific management for irrigated cotton. Abstract. p. 567—567. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf.,Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN.

 

E.     Precision agriculture proposals:

 

·        Water Management of Cotton in Precision Agriculture: Lint Yield as a Function of Site-Specific Irrigation. Robert J. Lascano. Amount requested $60,000 for one year. Proposal submitted to the Cotton State Support Committee.  (Proposal was funded for three years), 1999—2001

 

·        Data set for Cotton Production Model. Robert J. Lascano. Amount requested $4,330 for one year. Proposal submitted to the USDA-ARS. (Proposal was funded), 1999.

 

·        Yield Tracker: A yield mapping and prediction information delivery system. S. J. Maas, R. J. Lascano and D. Cooke. Proposal submitted to the IFAFS- USDA-CSREES. (Proposal was funded at $800,000 for three years).

 

·        Estimation of Profiles of Soil Water Content and Temperature From Radar Images. R. J. Lascano. Pre-proposal submitted to the Texas Higher Education ATP-ARP Program (Amount requested $240,000 for two years). Not Funded. (August, 2001).

 

·        Application of Geospatial and Precision Technologies. S. Maas, D.R. Krieg, and R.J. Lascano. Proposal submitted to IFAFS (Amount requested $1,254,670 for four years). Not funded. (July, 2001).

 

·        SWAT–Soil Water and Temperature Profiles of Bare Agricultural Fields. Robert J. Lascano, Stephan J. Maas, Susan A. Mengel, and Arthur L. Doggett. Proposal submitted to IFAFS (Amount requested $970,000). Not Funded.(July, 2001).

 

F.      Precision Agriculture meetings attended/papers (posters) presented:

 

·        Li, H., R.J. Lascano, E. Barnes, J. Booker, L.T. Wilson, E. Segarra, and K. F. Bronson. 2001. Temporal patterns of cotton reflectance and NDVI-days lint yield modeling. p. 590—594. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN. (Presented Paper)

 

·        Li, Hong, R. J. Lascano, Jill Booker, L. Ted Wilson, Kevin F. Bronson, and Eduardo Segarra. 2001. State-space description of underlying field heterogeneity on water and nitrogen use in cotton. Soil. Sci. Soc. Am. J. (In press). (Presented Poster)

 

·        Li, Hong, R.J. Lascano, L. T. Wilson, and E. Segarra. 2001. Semivariance and cross-correlation of sand, water, cotton canopy temperature, and plant reflectance in the landscape. In: Third European Conference on Precision Agriculture, 18—20 June 2001, Montpellier, France, p. 241—246. (Presented Paper)

 

·        Yu, Man, Eduardo Segarra, Susan Watson, Hong Li and R.J. Lascano. 2001. Precision farming practices in irrigated cotton production in the Texas High Plains. p. 201—208. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN. (Presented Paper)

 

·        Chua, T.T., K.F. Bronson, R.J. Lascano, J.W. Keeling, A.R. Mosier, J.P. Bordovsky, C.J. Green, and J.B. Booker. Abstract. p. 588—588. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf., Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN. (Presented Paper)

 

·        K.F. Bronson, J.W. Keeling, T. Wheeler, R.J. Lascano, P. Dotray, A. Brashears, S. Searcy, K. Siders, J.D. Booker, Jill Booker, R.K. Boman, Hong Li, and T. Chua. 2001. On-farm testing of site-specific management for irrigated cotton. Abstract. p. 567—567. In. P. Dugger and D. Richter (ed.) Proc. Beltwide Cotton Conf.,Anaheim, CA 9—13 Jan. 2001. Natl. Cotton Counc. of Am., Memphis, TN. (Presented Poster).

 

  1. Other developments