1. Introduction
American agriculture represents a highly productive enterprise, producing bountiful harvest for a growing population. However, closer inspection reveals U.S. agricultural production systems that are highly unstable, easily disrupted by weather, disease, and insects, and relies heavily on foreign trade. Cropping systems since World War II have become highly specialized, standardized, and simplified to meet increasing demands of the industrialized food system [
1,
2]. Many of these cropping systems are approaching monoculture systems that need to incorporate technological advances, high fossil fuel based inputs, and genetic engineering to remain sustainable. Nature’s plant and animal diversity is currently replaced with a small number of cultivated plants and domestic animals [
3].
Sustainable agriculture is not a constant state but is in a state of flux at all times; production systems that were sustainable twenty to thirty years ago are not sustainable today [
4]. The northern Great Plains is an example of constantly changing agriculture. Early settlers brought their tillage tools and annual cropping systems from the eastern U.S. to the northern Great Plains during the late 1890’s and early 1900’s. They soon learned that eastern U.S. cultural practices and cropping systems resulted in crop failure during dry periods and were not resilient, which led to the development of the wheat-fallow cropping systems to provide short-term production sustainability during dry years. We have since learned that fallow in cropping systems contributes to inefficient use of precipitation [
5] and soil resource degradation [
6]. Canadian scientists have shown that reducing the frequency of fallow and including legumes in the cropping system improved the overall sustainability of agricultural production in the semiarid northern Great Plains [
7].
Cropping systems specializing in one or two crops with little attention to crop diversity could lead to biological and physical soil degradation and ultimately soil chemical degradation [
2]. Annual cropping systems, which include diverse crops such as oilseeds, pulses, forbs, and forages, may be economically viable options for producers. Diversifying the plant community in cropping systems also influences the diversity of soil organisms and the soil environment. Enhancing biodiversity in agricultural systems can be a key ecological strategy to bring sustainability to cropping systems [
3]. Soil organisms and soil environmental changes resulting from diverse plant communities in cropping systems perpetuate biological synergies and adaptive management techniques inherent to multispecies systems [
8,
9]. Minimal attention has been given to efficient exploitation of synergism and/or antagonism in cropping systems [
10]. Attention to synergistic and/or antagonistic relationships of crops in cropping systems based on crop sequence or cropping patterns is crucial to bring sustainability and resilience to agricultural systems.
Objectives of our research were to determine if previous crop sequences have long-term benefits and/or drawbacks on spring wheat seed yield, seed N concentration, and seed precipitation-use efficiency in the northern Great Plains.
2. Materials and Methods
The research project was located at the Area IV Soil Conservation District/USDA-ARS Northern Great Plains Research Laboratory Research Farm about 6 km southwest of Mandan, ND (46° 46’ 22” N, 100° 57’ 09” W). Two sites (6.1 ha each) were chosen about 2 km apart on a Temvik-Wilton silt loam (fine-silty, mixed, superactive, frigid Typic and Pachic Haplustolls). Prior crops were a 3-year rotation of sunflower (
Helianthus annus L.)—spring wheat—spring wheat. During the establishment phase, sunflower was seeded using minimum-till techniques and spring wheat was seeded using no-till techniques. Inoculants, fertilizer rates, and other specific details for crop production are described by Tanaka
et al. [
11].
Research was initiated in 2002 by no-till seeding 10 crops (buckwheat [
Fagopyrum esculentum Moench], canola [
Brassica napus L.], chickpea [
Cicer arietinum L.], corn [
Zea mays L.], dry pea, grain sorghum [
Sorghum bicolor L.], lentil [
Lens culinaris Medik.], proso millet [
Panicum miliaceum L.], sunflower, and spring wheat) in adjacent strips to produce their respective crop residues (first year crop residue). The following year, the same 10 crops were no-till seeded perpendicular to the previous year, creating a 10x10 crop x crop residue matrix with 100 different crop sequences (second year crop residue) [
11]. In 2003, a second site of the three-year project was conducted using the same crop sequences as those used at the first site. The three-year crop sequences were run from 2002 to 2004 at site 1 and from 2003 to 2005 at site 2 (
Table 1 and
Figure 1). Spring wheat was uniformly no-till seeded at Site 1 in 2004 and Site 2 in 2005 after the 100 different crop sequence combinations. Using this crop matrix technique as a research tool allows for evaluation of multiple crop sequence effects in the same experiment under similar weather and soil conditions. Thus, spring wheat was no-till seeded over the crop residue of all crops included in the matrix. Crops were arranged each year using a randomized-complete block experimental design with a strip-block treatment arrangement and four replicates. The smallest experimental unit was 9 by 9 m. All crops, except corn and sunflower, were seeded using a no-till drill (model 750, John Deere, Moline, IL
2) with a 19-cm row spacing. Corn and sunflower were planted with a no-till row-crop planter in 76 cm rows.
Table 1.
Crops and sites used to evaluate influences of crop sequence on spring wheat production.
Table 1.
Crops and sites used to evaluate influences of crop sequence on spring wheat production.
Year | Crop | Site 1a | Site 2a |
---|
1 | Ten Cropsb | 2002 | 2003 |
2 | Crop matrix, ten cropsc | 2003 | 2004 |
3 | Spring wheat seeded over crop matrixd | 2004 | 2005 |
Figure 1.
A crop x crop residue matrix used to evaluate the influences of crop sequences on agronomic and environmental attributes [
11] (From
Agron. J. 99:904-911 (2007), with permission, copyright American Society of Agronomy). During the first year, 10 crops (numbered 1 through 10) were no-till seeded into a uniform crop residue. During the second year, the same 10 crops were no-till seeded perpendicular over the residue of the previous year’s crops. Individual plot numbers are assigned for each experimental unit in the replication.
Figure 1.
A crop x crop residue matrix used to evaluate the influences of crop sequences on agronomic and environmental attributes [
11] (From
Agron. J. 99:904-911 (2007), with permission, copyright American Society of Agronomy). During the first year, 10 crops (numbered 1 through 10) were no-till seeded into a uniform crop residue. During the second year, the same 10 crops were no-till seeded perpendicular over the residue of the previous year’s crops. Individual plot numbers are assigned for each experimental unit in the replication.
In late April of 2004 and 2005, spring wheat (cv. Amidon) was uniformly no-till seeded over Site 1 (2004) and Site 2 (2005) after the 100 different crop sequence combinations. Spring wheat was seeded at 3.2 million viable seeds ha
–1, with N fertilizer (78 kg N ha
−1 as ammonium nitrate) banded between every other row in 38-cm spacing and P fertilizer (11 kg P ha
−1 as triple superphosphate) with the seed at planting. Prior to seeding, weed control was accomplished using nonselective herbicide (glyphosate [N-(phosphonylmethyl) glycine] 1.1 kg a.i. ha
−1) for no-till. Post emergence weed control consisted of fenoxaprop-p-ethyl (d isomer) (70 g a.i. ha
−1) and 2, 4-D (dichlorophenoxyacetic acid, 350 g a.i. ha
−1) applied between Feeks growth stage 3 to 4 [
12]. In mid-August, seed yield was determined by harvesting 11.4 m
2 area with a plot combine. Seed N concentration was determined by sending a subsample to a commercial laboratory using the Dumas method for plant N analysis [
13]. Precipitation use efficiency (PUE), an integrative measure of crop sequence influences on water use by spring wheat, was calculated by determining the quantity of precipitation occurring from the harvest of one crop to the harvest of spring wheat divided into the actual spring wheat seed yield of each experimental unit.
A particular crop sequence determined the precipitation received from the harvest of one crop to the harvest of the following spring wheat crop. Merrill
et al. [
14] determined crop soil water use and soil water content of second year crops at harvest. Soil water remaining after harvest of second year crops was not part of the PUE calculation and may have influenced this following spring wheat production.
Statistical analysis (F test) indicated a significant year (site) x treatment interaction; therefore, each year (site) was analyzed separately (not shown). Spring wheat seed yield and grain N concentration were analyzed using the GLM procedure [
15]. Statistical comparisons within each evaluation were made with Least Significant Difference (LSD). Precipitation-use efficiency comparisons were made using Dunnett’s one-tailed test with continuous spring wheat (spring wheat—spring wheat sequence) as the control. Continuous spring wheat was considered to have the lowest yield potential. All statistical differences were evaluated at a probability level of ≤0.05.