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Agronomy Journal 92:321-328 (2000)
© 2000 American Society of Agronomy

SOIL MANAGEMENT

Nitrogen Management in No-Tillage Grain Sorghum Production

I. Rate and Time of Application

Raj Khoslaa, Mark M. Alleyb and Paul H. Davisb

a Dep. of Soil & Crop Sci., C4 Plant Sciences Building, Colo. State Univ., Ft. Collins, CO 80523 USA
b Dep. of Crop & Soil Environ. Sci., Smyth Hall, Virginia Polytechnic Inst. and State Univ., Blacksburg, VA 24061-0404 USA

rkhosla{at}lamar.colostate.edu


    ABSTRACT
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 
Grain sorghum [Sorghum bicolor (L.) Moench] is grown in rotation with wheat (Triticum aestivum L.) and soybean [Glycine max (L.) Merr.] in the mid-Atlantic. Sufficient data on N fertilization of sorghum are not available for this region. Our objective was to evaluate the influence of multi-rate N fertilization on dryland sorghum. Treatments consisted of factorial combinations of four starter-band N rates (11, 34, 56, and 78 kg N ha-1) and four sidedress N rates (0, 45, 90, and 134 kg N ha-1). A broadcast treatment of 67 kg N ha-1 at planting was also included. Starter-band was applied 5 cm to the side and below the seed. Sidedress was applied 35 days after emergence at the eight-leaf growth stage. Grain yield ranged from 1.7 to 11.9 Mg ha-1 over eight site-years and was responsive and nonresponsive to N applications on four sites each. Nonresponsiveness was either due to high levels (>85 kg N ha-1) of residual soil mineral N, or severe water stress conditions. Our results indicate that production of sorghum on soils testing high in mineral N (50 kg N ha-1 in the surface 0.3 m) at planting should not receive any starter-band N in conjunction with sidedress N application of 130 kg N ha-1 for optimum economic return to N fertilization. For soils testing low in mineral N, 40 kg N ha-1 starter-band in conjunction with 130 kg N ha-1 sidedress N should optimize the sorghum yields in most situations.

Abbreviations: ANOVA, Analysis of variance • DAP, days after planting • UAN, urea ammonium nitrate


    INTRODUCTION
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 
GRAIN SORGHUM is a relatively new crop to Virginia. It has been recognized as a more drought-tolerant crop (Bennett et al., 1990, p. 3–9; Khosla et al., 1995) and therefore a potential alternative to corn (Zea mays L.). Grain sorghum is grown on about 6000 to 10000 ha in Virginia, mostly under no-tillage systems for erosion control and for more efficient use of available soil-water. However, land area planted to grain sorghum has not increased, partially because production practices to increase yields in no-tillage systems are lacking.

One factor that continues to be a problem in high-residue (no-till) farming systems is N fertilizer management (Lamond et al., 1991). No-till systems often exhibit suppressed yields because of lesser N availability (Rao and Dao, 1996). This occurs because of slower N mineralization (Phillips et al. 1980), greater N immobilization (Rice and Smith, 1984), denitrification (Rice and Smith, 1982), and NH3 volatilization (Terman, 1979). Also, below-optimum soil temperatures in no-till environments cause lower nutrient availability in the early part of the growing season (Gordon and Whitney, 1995). All these complexities with N fertilizer management in no-tillage systems indicate the need for more research for improved and efficient utilization of fertilizer N.

Opportunities to incorporate N fertilizer below the residue layers in reduced-tillage systems are limited (Mengel et al., 1982). Consequently, the most common application method used in no-tillage systems is broadcasting either solid ammonium nitrate or urea, or spraying urea ammonium nitrate (UAN) solutions on the soil surface immediately before or after planting (Mengel et al., 1982). However, surface application of N fertilizer can result in significant N losses through ammonia volatilization.

Several studies (Eckert, 1987; Fox and Piekielek, 1987; Fox et al., 1986; Maddux et al., 1984; Bandel et al., 1980 and 1984; Mengel et al., 1982) have examined placement methods for no-tillage corn production in the mid-Atlantic region, the Corn Belt and the Great Plains. They reported that similar N application rates of broadcast UAN produced lower yields than either injected or surface-banded UAN. Possible N loss mechanisms noted with broadcast UAN include volatilization and immobilization (Lamond et al., 1991). Much less work has been done on N fertilizer management for grain sorghum in no-tillage systems.

Studies with grain sorghum (Lamond, 1987; Sweeney, 1989) have shown that knifed N–P–K applications at planting increased grain sorghum yields relative to broadcast applications in high-residue systems. These results for grain sorghum, coupled with those reported for other crops [i.e., corn, barley (Hordeum vulgare L. subsp. vulgare) (Tomar and Soper, 1981; Malhi and Nyborg, 1990), and wheat (Diebert et al., 1985; Rao and Dao, 1992 and 1996)] have consistently shown that surface-band-applied N fertilizer is more efficient than surface broadcast-applied N. However, in the mid-Atlantic region, the majority of crops are grown on sandy coastal plain soils with low organic matter content (generally <20 g kg-1) and sandy to sandy loam surface (Gilliam and Boswell, 1984). Therefore, it is not advisable to band-apply the total amount of fertilizer N needed by the crop at the time of planting, because of the potential for high N leaching and denitrification losses.

A possible means to increase the fertilizer N efficiency for humid regions is to split-apply the fertilizer N. The sidedress application, N fertilization several weeks after corn emergence, has maximized the efficiency of fertilizer N in most situations (Piekielek and Fox, 1992; Fox et al., 1986; Aldrich, 1984; Olson and Kurtz, 1982). Also, the presence of plants at the time of side-dressing application reduces NH03 volatilization loss by shading and absorption of some of the evolved NH03 (Harper et al., 1983).

The period of rapid growth and nutrient uptake by grain sorghum plants occurs about 35 d after emergence (Vanderlip, 1993) at the eight-leaf growth stage. Sidedress application at this stage is feasible and would be beneficial for the crop. However, the need for N fertilizer application at the time of planting grain sorghum under a no-tillage system should not be ignored. The layer of crop residue on the soil reduces soil temperature (Unger, 1978; Thomas et al., 1973) and may sometimes lower the nutrient availability in the early part of the growing season (Gordon and Whitney, 1995). Application of starter-band fertilizer N within the rooting zone of the young seedlings has been shown to be efficient and beneficial to the crop (Lamond and Whitney, 1991). In a more recent study, Gordon and Whitney (1995) reported an 18% grain yield increase by application of fertilizer N in a starter band. Similar research is lacking in the mid-Atlantic Coastal Plain region.

Our overall objective was to evaluate the influence of multirate N fertilization on dryland grain sorghum production, and to determine the optimum N fertilization rates for maximum economic grain yields. Specific objectives were to: (i) determine the optimum rate of band-placed starter N fertilizer needed in combination with sidedress N applications to achieve maximum economic grain yields; (ii) evaluate whether preplant broadcast N applications are as efficient as band-placed and sidedress N applications used together; and (iii) estimate profit associated with N fertilizer use as a function of starter-band and sidedress N rates.


    Materials and methods
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 
Field studies were conducted in multiple locations to study the effects of rate and time of fertilizer N application on no-till grain sorghum yield during 1995, 1996, and 1997. Experimental plots were located on producers' fields at different locations in the Virginia Coastal plain. The sites were representative of the soils (loamy sand or sandy loam, with low plant-available water holding capacity and <20 g kg-1 organic matter) widely used for grain sorghum production in Virginia (Table 1) . The experimental plots were laid out in a randomized complete block design with four replicates of each treatment. Each experimental plot consisted of eight 0.38-m-wide rows that were 7.62 m in length. Planting was done during the third and fourth week of May each year. Cultivar Pioneer Brand 8118 was planted on the Pamunkey and Conetoe soil in 1995, and cultivar Pioneer Brand 8310 was planted on all other soil types in 1996 and 1997. Seed were planted approximately 2 cm deep.


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Table 1 Location, year, soil classification, and selected chemical properties of the surface 0 to 0.15 m of the soils utilized in this study

 
Soil samples were collected at planting to a 0.9-m depth in increments of 0 to 0.15, 0.15 to 0.3, 0.3 to 0.6, and 0.6 to 0.9 m using a JMC Backsaver1 (Clements Associates, Newton, IA) probe. A total of 16 cores for each depth increment were composited. Composite samples were extracted with 2 M KCl and the extracts were analyzed for soil nitrate and ammonium by the Salicylate and Griess-Illosvay methods, respectively (Keeney and Nelson, 1982), using an Automated Ion Analyzer (Zellweger Analytics, Lachat Instruments Div., Milwaukee, WI). Soil mineral N values were expressed in kg ha-1 using a bulk density estimate of 1.6 Mg m-3, an average of numerous samples collected at various depths from these and similar coastal plain soils (Scharf, 1993).

Nitrogen treatments consisted of factorial combinations of four starter-band N rates at planting and four sidedress N rates at the eight-leaf growth stage to supply a total of 10 different N fertilization rates (11, 34, 56, 78, 101, 123, 146, 168, 190, and 213 kg N ha-1) and a broadcast rate of 67 kg N ha-1 at the time of planting. Urea ammonium nitrate solution was used as the N fertilizer source. Starter-band treatments were placed 5 cm below and to the side of the seed with a standard single disk opener using a carbon dioxide-pressurized system mounted on a John Deere Max Emerge 2 Conservation tillage planter (Deere and Co., Moline, IL). Phosphorus fertilizer solution (in the form of 10-34-0 ammonium polyphosphate) was also placed with the starter-band N. Potassium chloride was broadcast at each site at 67.2 kg K2O ha-1 rate to ensure adequate K availability.

Sidedress N was applied approximately 35 days after planting (DAP) at the eight-leaf growth stage of grain sorghum plants. The UAN solution was applied with a carbon dioxide-pressurized backpack sprayer whose spray nozzles were fitted with Teejet raindrop spray tips (Spraying Systems, Wheaton, IL). Flow rates for each tip size were measured at each experimental location prior to N application. Proper walking speed to obtain the desired application rate was calculated, and a stopwatch and metronome were used to calibrate and maintain proper walking speed during N application. Broadcast treatment application of 67 kg N ha-1 was done in the same manner at the time of planting.

Harvesting was done between the third week of September and the first week of October every year. Grain sorghum yield was determined by harvesting the four middle rows of each plot with a plot combine. Grain moisture contents were measured on all samples with a GAC II grain moisture meter (Dicky John, Auburn, IL). Grain yields are reported at 140 g kg-1 moisture content. On-site weather data including daily rainfall and daily maximum and minimum temperatures were recorded with Weather Monitor II automated weather systems (Spectrum Technologies, Plainfield, IL).

Analysis of variance (ANOVA) on grain yield was done using the SAS software package (SAS Inst., 1993) to test for significant treatment effects. When ANOVA results indicated significant effects at the 0.05 probability level, mean separation of grain yield was performed by Duncan's multiple range procedure (SAS Inst., 1993). Data were further analyzed via quadratic regression procedures with SAS (SAS Inst., 1993) and Sigma-Stat (Jandel Scientific, San Rafael, CA) to determine the optimum rate of starter-band N fertilizer in combination with sidedress N applications, and to compare starter-band with broadcast N application at planting. To determine the estimated profit associated with N fertilizer use as a function of starter-band N rate and sidedress N rate, the least square quadratic response surface regression (RSREG procedure) was calculated for each location using SAS (SAS Inst., 1993). The rate corresponding to the highest point on this response surface was the economic optimum (Scharf and Alley, 1993). The economic optimum N rate at planting (starter-band N) in combination with the sidedress N rate was calculated from this regression equation. Profit was estimated as grain sorghum value (yield x grain price) - N fertilizer cost (total N rate x N price) - other production costs (estimated as $345 ha-1 for all experiments). Current price was taken as $9.56 Mg-1 of grain sorghum and as $0.55 kg-1 of fertilizer N.


    Results and discussion
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 
Selected chemical analyses of surface soil samples taken from all locations at grain sorghum planting are presented in Table 1. The surface organic matter content ranged from 11 to 24 g kg-1. Based on Mehlich-1 extractions, all soils tested high (>18 mg kg-1) in P and medium to high in K, Ca, and Mg (Donohue and Heckendorn, 1994). The soil pH to a depth of 0.9 m ranged between 5.5 and 7.4, making it very suitable for crop root growth. Plant-available water holding capacity of these soils varied from low (Pamunkey sandy loam ~125 mm water m-1 soil) to very low (Bojac sandy loam ~50 mm water m-1 soil) (Khosla and Persaud, unpublished data, 1998). These soils are deep and well drained and are susceptible to leaching of nitrates.

Climatic conditions varied during the three years (1995, 1996, and 1997) of this project (Fig. 1) . Rainfall during two (1995 and 1997) out of three years was much below average (average rainfall ranges between 100 and 150 mm per month based on 30 yr of rainfall data, Norris, 1985). The early part of the growing season (May to June) in 1995 was conducive to germination, emergence, and vegetative growth (i.e., temperatures were above the critical temperature of >=10°C for grain sorghum growth) (Anda and Pinter, 1994). Grain sorghum stands on both soils, the Pamunkey sandy loam and the Conetoe loamy sand, were excellent. However, the months of July and August were extremely hot and dry (32–38°C daytime temperatures) and plants were severely water stressed. In 1997, conditions were dry throughout the growing season with very little rainfall [203 mm and 260 mm at two sites, Atlee and Kempsville, respectively (Fig. 1)]. Temperatures were below normal during the month of May and planting was therefore delayed by about 2 wk. However, on Bojac soil, temperatures stayed below or around the 10°C critical level through the week after the emergence of grain sorghum. This low temperature induced tiller growth in grain sorghum later in the season, consequently increasing the water requirement of the crop. Water stress symptoms in plants were more prominent in 1995 and 1997 and were particularly evident in the plants growing on the Conetoe loamy sand, Bojac sandy loam, and Atlee very fine sandy loam. In 1996, conditions were good overall, with normal to above-average rainfall (>=550 mm) during the growing season at all locations (Fig. 1).



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Fig. 1 Rainfall distribution during the growing period of sorghum for Virginia soils (A) Pamunkey sandy loam and Conetoe loamy sand, 1995; (B) Suffolk fine sandy loam, 1996; (C) Bojac sandy loam, 1996; (D) Appling-Cecil complex, 1996; (E) Atlee very fine silt loam, 1997; and (F) Kempsville fine loamy, 1997. Weather data for Wheeling silt loam was not available

 
Grain yields over 3 yr on eight different sites varied from as low as 1.7 Mg ha-1 to as high as 11.9 Mg ha-1 (Table 2) . An overall average of the highest yield at eight locations was 7.98 Mg ha-1 and is testimony to good cultural practices and fertility levels for plant nutrients other than N. The grain sorghum crop was highly responsive (the difference between the yield at no N application and the highest yield of >3 Mg ha-1) to N fertilizer applications on three soils (Suffolk, Bojac, and Appling-Cecil), moderately responsive (yield response between 1 and 3 Mg ha-1) on one soil (Wheeling), nonresponsive (no treatment yield more than 1 Mg ha-1 above the control yield) on two soils (Pamunkey and Atlee), and negatively responsive (treatment yields below the control yield) on two soils (Conetoe and Kempsville). Figure 2 shows the yield response of grain sorghum to sidedress N applications at selected sites and illustrates the above-mentioned four categories of yield response, similar to the method of Scharf (1993).


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Table 2 Nitrogen fertilizer levels and sorghum grain yield for eight soil types in Virginia during 1995, 1996, and 1997

 


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Fig. 2 Sorghum grain yield responses to side-dress N applications on different soil types in Virginia during 1995, 1996, and 1997. (A) Suffolk sandy loam is characterized as highly responsive, (B) Wheeling silt loam as moderately responsive, (C) Pamunkey sandy loam as nonresponsive, and (D) Conetoe loamy sand as negatively responsive

 
Among the four responsive soils, grain yield reached the point of diminishing returns on only two soils, Suffolk and Appling-Cecil complex (Fig. 3a and 3c) . Conversely, the grain yields generally did not reach the point of diminishing returns on the Bojac and Wheeling soils (Fig. 3b and 3d). The grain yields were still increasing linearly in response to all applications of fertilizer N. This linear response of grain yield to applied N could be attributed to heavy rainfall (510 mm; Fig. 1) during the growing season that provided abundant plant-available soil moisture for plant growth and at the same time may have caused leaching of nitrates.



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Fig. 3 Yield response to sidedress N applications and response surface curves describing estimated relative profit due to N applications (starter-band N and sidedress N) on (A) Suffolk fine sandy loam, (B) Bojac sandy loam, (C) Appling-Cecil complex, and (D) Wheeling silt loam in Virginia in 1996

 
Review of the estimated relative profit response surface in Fig. 3 reveals that the crop reached its maximum economic yield at starter-band and sidedress N application rates of 39 and 134 kg N ha-1 on the Suffolk soil, 0 and 135 kg N ha-1 on the Bojac soil, 0 and 106 kg N ha-1 on the Appling-Cecil complex, and 0 and 129 kg N ha-1 on the Wheeling soil (Fig. 3a, 3b, 3c, and 3d, respectively). Maximum economic yield achieved at zero level of starter-band N in combination with a sidedress N rate on three soils indicates that grain yields at these sites did not respond to starter-band N applications. The Bojac and Wheeling soils had >=70 kg N ha-1 of mineral N in the surface 0.3 m, out of a total >105 kg N ha-1 of profile mineral N (Table 3) . This level of residual mineral N evidently provided sufficient N to support the early-season growth of the grain sorghum plants prior to side-dressing.


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Table 3 Residual soil mineral N (NO3–N plus NH4–N) by depth present at grain sorghum planting for eight experimental sites in Virginia

 
Conversely, grain yields on Suffolk fine sandy loam did respond to starter-band N (Fig. 3a). Residual mineral N of 45 kg N ha-1 in the top 0.3 m of the Suffolk soil at planting was not sufficient to provide N support to the crop until it received side-dressing at 35 DAP. Also, heavy rainfall (607 mm, Fig. 1) during the season on the sandy textured Suffolk soil may have caused leaching of nitrates. The Appling-Cecil complex had an amount of residual mineral N at planting (51 kg N ha-1) similar to the Suffolk soil. However, the Appling-Cecil complex is a heavy texture clay loam soil underlying the sandy loam surface horizon; hence, the leaching potential of this soil is much lower (L.W. Zelazny, personal communication, 1998) than that of the Suffolk soil. This is apparent to some extent because grain sorghum did not respond to starter-band N; also, the point of maximum yield on the Appling-Cecil complex occurred at 106 kg N ha-1 sidedress N, compared with >=130 kg N ha-1 sidedress N on other sandy textured soils. Also, the total profile mineral N in the Appling-Cecil complex was 131 kg N ha-1, which is 48 kg N ha-1 higher than the level in the Suffolk soil (Table 3).

Residual mineral N present in the top 0.3 m of soil at planting is crucial in deciding whether or not starter-band N should be applied. Residual mineral N levels of >45 kg N ha-1 in the surface 0.3m of soil in this study were sufficient to support the crop growth until side-dressing. The optimum rate of starter-band N fertilizer needed in combination with sidedress N applications to optimize grain yields therefore depends on the amount of soil mineral N at planting. Based on the data from these experiments, for soils testing high in mineral N (>=50 kg N ha-1 in the surface 0.3 m of soil) at planting, zero starter-band N should be applied in conjunction with sidedress N applications of 130 kg N ha-1. For soils testing low (<50 kg N ha-1 in the surface 0.3 m of soil) in mineral N at planting, starter-band N application of 40 kg N ha-1 in conjunction with 130 kg N ha-1 sidedress should optimize the grain sorghum yields under conditions similar to those in our study.

The efficiency of preplant broadcast N application as compared with starter-band N plus sidedress N applications could not be evaluated extensively here. Lack of yield response to N fertilization on four sites in 1995 and 1997, and to starter-band N on three out of four sites in 1996, prevents any assessment of the efficiency of the fertilizer placement methods. However, the Suffolk fine sandy loam experiment conducted in 1996 showed that the grain yield response to broadcast N applications and starter-band applications were not significantly different (Table 2). The average grain yields on the Suffolk soil from starter-band N and broadcast N at planting were 8.05 and 7.95 Mg ha-1, respectively, suggesting that broadcast N applications were as efficient as band-placed and sidedress N applications. This finding contradicts those reported by other researchers (Lamond, 1987; Sweeney, 1989; Malhi and Nyborg, 1990; Lamond and Whitney 1991; Lamond et al., 1991; Rao and Dao, 1996). However, the results on the Suffolk soil can probably be attributed to significant rainfall that occurred soon after planting and continued for the next several days. Consequently, little or no NH3 volatilization losses or fixation in the surface mulch would be expected. The success of broadcast N applications probably depends on rainfall shortly after N applications. Chichester and Morrison (1995) reported similar results from their 2-yr study in Temple, TX.

Response surfaces describing the estimated profit due to N application as a function of N fertilizer rates at planting (starter-band) and side-dressing are shown for four experimental locations (Fig. 3). The highest point on the response surface for Suffolk soil (Fig. 3a) corresponds to a maximum estimated profit of $341 ha-1, obtained by application of 39 kg ha-1 of starter-band N and 135 kg ha-1 of sidedress N fertilizer. There is an increasing trend in the yield response to applied fertilizer N for both starter-band and sidedress applications on Suffolk soil (Fig. 3a). Conversely, on the Bojac soil there is a decreasing trend in the estimated profit with the increase in the application rates of starter-band fertilizer (Fig. 3b). Starter-band N did not increase the estimated profit because the grain yield increases due to starter band were not great enough to cover the cost of the added fertilizer N. However, each additional sidedress N application significantly increased the estimated profit. The highest point on the response surface corresponds to the maximum estimated profit of $402 ha-1 obtained in this experiment by application of 0 kg ha-1 of starter-band N and 135 kg ha-1 of sidedress N fertilizer (Fig. 3b). Trends in estimated profit similar to those reported for the Suffolk and Bojac soils were found for the Appling-Cecil complex and Wheeling soils (Fig. 3c and 3d).

Nonresponsiveness or negative-responsiveness of grain sorghum yields in four out of eight site-years of this study can be attributed to high levels of residual mineral N present in the soil profile at planting. Also, erratic rainfall patterns that promoted early season luxuriant crop growth on low plant-available water holding capacity soils caused severe water stress conditions later in the season. These conditions translated growth into early leaf senescence and poor head development and grain filling. Consequently, the grain yields were lower and nonresponsive to applied N fertilizer.

Residual mineral N is usually neglected in the humid mid-Atlantic region in making fertilizer N recommendations due to the widely accepted perception that over-winter soil mineral N losses are high (Bundy and Malone, 1988; Gilliam and Boswell, 1984). However, residual soil mineral N was found in significant amounts in the top 0 to 0.9 m of the soil profile at planting for four nonresponsive sites. In light of the above-mentioned results, it would be unwise to ignore soil residual mineral N at planting. There were 147 and 112 kg of mineral N ha-1 in the Pamunkey and Conetoe soils, respectively, in 1995. Similarly, there were 129 and 87 kg of mineral N ha-1 in the Atlee and Kempsville soils, respectively, in 1997. These high residual N levels probably reflect N that mineralized from the previous soybean crop and native organic matter. Mineral N in the deeper (0.6–0.9 m) horizon could mostly have come from previous N fertilizer applications. Lack of yield response to applied N on four sites is therefore reasonable because of below-average rainfall conditions during the growing season and relatively high residual mineral N levels that were present at these four sites at the time of planting. Even with normal rainfall conditions on these four sites, it is highly unlikely that grain sorghum will respond to starter-band N application when soil mineral N levels exceed 50 kg N ha-1 in the surface 0.3 m at planting as observed at other sites in this study. These agronomically significant levels of soil profile mineral N warrant consideration in developing improved and more efficient N fertilizer recommendations for no-till grain sorghum production on sandy soils in the mid-Atlantic region. A system for incorporating soil mineral N as an integral part of the N recommendation system for no-till grain sorghum is presented in an associated paper (Khosla and Alley, 2000).

The challenge of dryland grain sorghum production in the mid-Atlantic region is to synchronize the plant N need with plant-available water. This can perhaps be achieved by partitioning the N application of the crop into several doses. Our findings indicate that little (<=30 kg N ha-1) or no starter-band N should be applied to soils testing high (>=50 kg N ha-1) in residual mineral N at the time of planting, while the remaining N fertilizer should be applied in smaller amounts as sidedress N applications at various growth stages of the crop. This will restrict plants from accumulating excessive biomass early in the season and may reduce the risk of severe water stress later in the season. Sidedress N in this experiment was applied at the eight-leaf growth stage that occurs about 35 DAP. Another period of rapid growth and nutrient uptake in grain sorghum occurs at the midbloom growth stage, around 60 d after emergence (Vanderlip, 1993). Should rainfall occur during this period, sidedress N application to the crop at midbloom stage can be applied with a high-clearance applicator. Although the window of opportunity that exists at this stage is relatively short, it could promote proper head development and enhance grain yield and N use efficiency of the crop.SAS Institute 1993


    ACKNOWLEDGMENTS
 
This research was supported by the Fluid Fertilizer Foundation. Appreciation is expressed to James Hammons for assistance with field layout and experimentation.


    NOTES
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 
1 Mention of a trade name neither constitutes endorsement of the equipment or products used nor criticism of similar ones not used or mentioned by the authors or Virginia Polytechnic Institute and State University. Back

Received for publication January 25, 1999.
    REFERENCES
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and methods
 NOTES
 Results and discussion
 REFERENCES
 




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The Plant Genome