1. Introduction
Cover crops are a key component of conservation agriculture, and they must be managed appropriately to optimize their benefits, which include increased water infiltration and reduced soil erosion, runoff, and soil compaction [
1,
2]. Warm-season cover crops provide similar benefits as cool-season cover crops, but fast-growing summer cover crops that generate large amounts of biomass provide increased potential for weed suppression; otherwise, weeds can spread rapidly and compete with main crops [
3]. Droughts are also more likely to occur in summer months due to increased temperatures and sporadic rainfall, especially in the southeastern US; therefore, it is important to select cover crop species that are drought tolerant and can produce optimum biomass. In addition, warm-season cover crops provide a significant contribution to biodiversity, creating ecological balance, helping to alleviate plant diseases and destructive insects. Beneficial insects, birds and amphibians feed on warm-season cover crops and reproduce during the summer growing season [
3,
4].
Rollers/crimpers have been used in conservation farming systems to mechanically terminate cover crops at an appropriate growth stage by flattening and crimping plant tissue at equal intervals with crimping bars mounted evenly around the roller’s cylindrical drum. After cover crops have been crimped, plant desiccation results in dry residue that forms a thick mulch that covers the soil surface. In agroecosystems where water for crop production is in short supply, flattened cover crops can be left on the soil surface and used as a mulch to conserve water by shading and cooling the soil surface. This reduces the evaporation of water from the soil surface. Mulching is a technique that involves covering the soil with a layer of organic material (cover crop residue). Mulching has several benefits including retaining moisture by preventing water evaporation, suppressing weeds by blocking sunlight and not allowing weed seeds to germinate, improving soil health by adding nutrients and organic matter to the soil, preventing soil erosion by reducing the impact of raindrops on the soil surface, and regulating soil temperature by keeping the soil cooler in hot weather conditions in Alabama. Benefits from this soil coverage include reduced soil erosion, reduced weed germination and growth, and soil water conservation for the following cash crop that can be planted directly into cover crop residue [
5,
6,
7]. In Alabama, rolling/crimping should be performed at least 21 days before planting a cash crop into rolled residue since this period is needed to prevent the cover crop from competing for soil moisture and nutrients [
6,
8]. Results from a field study [
6] indicated that due to accelerated rye senescence, rye termination rates above 90% were sufficient to plant a cash crop. To speed up the cover crop termination process, producers utilize herbicides to supplement rolling/crimping. However, in organic vegetable production, commercial herbicides cannot be used. Thus, terminating cover crops mechanically must be as efficient as chemical termination and might require multiple passes with roller/crimper over the same cover crop area to obtain the recommended cover crop termination rate above 90%.
Moreover, the farming community has been questioning if recurrent rolling/crimping over the same cover crop could cause soil compaction issues. Previous research has shown that multiple passing of agricultural equipment over the same area of a field causes soil compaction and contributes to significant soil degradation such as soil structure deformation by decreasing porosity and increasing bulk density [
9]. Research conducted by [
10] has shown that the soil quality deteriorated either with a greater number of passes by a lighter tractor or by a heavy tractor with fewer passes. According to [
11], conventional tillage operations are known to have the most negative effect on causing soil compaction, which is associated with serious global environmental problems due to the degradation of the soil structure, which lowers water infiltration and hinders plant growth.
Field research that was conducted by [
12] compared the long-term effects of conventional and conservation tillage practices on silty loam soil properties in Germany. These researchers concluded that the recurrent deep impact of tillage tools in conventional tillage plots caused the permanent destruction of freshly developed soil aggregates. Consequently, a relatively weak soil structure in the tilled soil layers proved unable to support an applied single-wheel 2.5-ton dynamic load. Conversely, in the conservation tillage plots, soil was able to adequately handle a 2.5-ton wheel load due to a strong aggregate system and did not lead to structural soil degradation. The effects of conventional, minimum, and zero-tillage on soil water, soil organic matter, and soil compaction were evaluated by the authors of [
13]. They found that the zero-tillage treatment conserved much more soil water than conventional and minimum-tillage treatments, especially in dry years. Additionally, for conventional tillage, a soil compaction restrictive layer was detected in the subsoil compared to the topsoil. Field experiments conducted by [
14] indicated that the soil strength limit for unrestricted root growth for cotton is 2.0 MPa, particularly for higher soil moisture content, where the difference in soil resistance for root penetration between compacted soil (with traffic) and uncompacted soil (no traffic) is low.
To address farm needs associated with managing summer cover crops in no-till systems, a field experiment was initiated at the NSDL in Auburn, Alabama, to evaluate the effectiveness of a two-stage experimental roller/crimper in terminating two warm-season cover crops. For this field experiment, the legume, iron clay pea (
Vigna unguiculata, L.), and grass, pearl millet (
Penninsetum glaucum, L.), were selected. Iron clay pea has been used in Alabama as a popular summer legume cover crop due to it having excellent soil erosion and weed control. It also provides good protection from soil compaction, and it is a heat- and drought-resistant plant during hot summer months but does not perform well in excessively wet soil [
15,
16]. In addition, this legume can produce 110 to 160 kg of nitrogen ha
−1 [
17,
18]. Pearl millet is a warm-season annual bunchgrass with a height ranging from 1.8 m to 2.1 m that scavenges nitrogen, protects from soil erosion, and suppresses weeds in the summer. This plant is well suited to grow on many different soils, including clay soils, as it can break up compacted soil and develops a deep root system that can survive under water shortage [
19,
20,
21].
According to [
22], pearl millet has the highest biomass growth potential compared with other types of millet. The objective of this study was to determine the effects of number of rolling passes (rolling once, twice and three times over the same area) with a two-stage roller/crimper on iron clay pea and pearl millet warm-season cover crop termination, volumetric soil moisture content (VMC), and soil compaction.
2. Materials and Methods
A three-year experiment, carried out over the 2015–2017 growing seasons, was initiated at the National Soil Dynamics Laboratory (NSDL), Auburn, Alabama USA, (latitude north: 32.6; longitude west: −85.5), which has a subtropic climate. The effectiveness of a patented two-stage roller/crimper prototype [
23] (
Figure 1) in terminating iron clay peas and pearl millet with recurrent passes over the same cover crop area was evaluated. The experimental layout was a randomized complete block design with treatments randomly assigned to each block with four replications, where rolling treatments were considered fixed effects and blocks (replications) were considered random effects.
Each experimental plot area was 465 m2 (0.0465 ha) and both cover crops were broadcast in each growing season to the entire plot area with 5.9 kg of seed for iron clay pea and 3.2 kg of seed for pearl millet utilizing a chest spreader for all three seasons. Planting rates per hectare were 127 kg/ha for iron clay peas and 68 kg/ha for pearl millet. Then, seeds were tilled in (incorporated) and packed in with a steel mesh (basket) roller to provide a level surface and good seed-to-soil contact. A total of 16 plots with dimensions of 6.1 m long by 1.8 m wide were comprised in the field experiment.
Field testing of the two-stage roller/crimper was conducted on the soil bins at NSDL. The two-stage roller/crimper [
23] comprises two drums, with the first being a smooth drum that flattens the cover crop on the soil surface, and the second drum, with equally spaced crimping bars on the drum’s circumference, crimps stems and flattens the cover crop. The crimping principle is based on applying vertical force generated by the weight of the drum to the cover crop against a firm soil surface. To increase the crimping effectiveness, the second drum assembly with crimping bars is also preloaded with two compression springs on each end of the drum. When the roller/crimper moves forward, springs are compressed and decompressed (due to advancing from one crimping bar to the next), and they release their kinetic energy as a downward force (perpendicular) to the laying down cover crop, causing injury (crushing tissue) to the cover crop at equal intervals.
Identical experimental designs were employed for each cover crop on two adjacent soil bins (specialized testing areas specific to the NSDL constrained by metal I-beams), Iron clay peas were planted on a sandy loam soil (Hiwassee sandy loam: a clayey kaolinitic thermic (oxidic) Typic Rhodudults with 73% sand, 11% silt, and 16% clay). The sandy loam soil was designated to grow iron clay pea cover crop as this summer legume grows best on sandy soils and full sunlight [
15,
17,
18]. Pearl millet was planted on a clay soil (Davidson clay: a clayey kaolinitic thermic (oxidic) Rhodic Paleudults with 25% sand, 31% silt, and 44% clay). Clay soil was chosen to grow pearl millet as it can grow very well on many different soils including clay soils [
20,
21].
Field activities for each growing season are presented in
Table 1.
As depicted in
Figure 1, the two-stage patented roller/crimper prototype [
23] was a 3-point hitch mounted on the John Deere 4710 4-wheel drive tractor (34.5 kW).
Rolling/crimping treatments included rolling once, twice and three times operated at a speed of 5.0 km h−1, completed on the same day. Cover crop termination rates were assessed at zero (day of rolling/crimping treatment application), one, two, and three weeks after rolling and were compared to untreated cover crops (control). To evaluate cover crop termination rates, a handheld chlorophyll meter (SPAD 502 light sensor-based, Konica-Minolta; Ramsey, NJ, USA) was used to measure chlorophyll activity or “greenness” of cover crops. Termination rates were evaluated on a scale of 0% (no plant injury symptoms: green plant) to 100% (complete plant death: zero greenness).
Three chlorophyll measurements were taken of the leaves in each plot. The first measurement was collected close to the centerline of the plot (lengthwise) approximately 0.5 m from the plot edge, the second was obtained about 2.0 m from the first one, and the third one was taken also 2.0 m from the second one (about 0.5 m from the end of the plot). The leaf selection was based on a representative sample chosen randomly in proximity to the plot centerline. The average value from three samples was reported for each plot. Termination rate measurements were taken at the same time going through the 16 plots, completing 48 measurements. All 48 measurements required approximately one hour to complete.
Quantitative values for plant condition at 100% termination rate were determined with 10 measurements of a randomly selected cover crop leaf (10 leaves) using the chlorophyll meter SPAD 502 along with visual observations confirming that the plant tissue was dead. Termination assessment using SPAD 502 started with 10 leaves of each cover crop when it was green (0% termination). Then, every day, as cover crops changed in appearance (color and moisture), these measurements were repeated. When no changes in the chlorophyll meter’s readings were observed, the termination rate was assumed to be 100%;
Figure 2a,b show 0% (green) and 100% (dead) for iron clay peas, and
Figure 3a,b show 0% (green) and 100% (dead) for pearl millet, respectively. For chlorophyll meter values expressing termination rates between 0% and 100%, a graphical representation of chlorophyll data was performed in Excel to establish the best-representing equation relationship for that graph.
Results indicate the best fit for chlorophyll meter data for both cover crops were linear relationships. Based on instrument readings and knowing full greenness (0% termination rate) and full desiccation (100% termination rate), to calculate termination rates for summer cover crops between 0% and 100%, a linear relationship between instrument readings and termination rates was established and used to obtain the plant termination rate (%):
* Instrument reading range: 3.96–62.1
** Instrument reading range: 2.90–56.7
For the cover crop termination assessment and for volumetric soil moisture content (VMC) measurement, three measurements per plot were completed. Having 4 replications per treatment, a total of 12 measurements for each treatment were obtained. Then, the average value from three measurements for termination rate and VMC were reported for each plot.
On the day of rolling, the cover crop plant height was measured at eight randomly selected locations within each plot, and these values were averaged for each plot area (6.1 m × 1.8 m). The biomass was collected from one representative location in each plot using a 0.25 m2 area (0.5 × 0.5 m) steel wire frame. The cover crop biomass samples were oven-dried for 72 h at 55 °C using an electric oven (Model No. SC-350, Grieve Corporation, Round Lake, IL, USA). Termination rates were evaluated 0, 7, 14, and 21 (week 0, 1, 2, and 3) days after rolling (DAR). Soil volumetric moisture content (VMC) was measured 0, 7, 14, and 21 DAR using a portable time domain reflectometry (TDR) moisture meter with 12 cm-long rods (Spectrum Technologies, Plainfield, IL, USA).
Soil strength was measured with a FieldScout SC900 soil compaction meter (Spectrum Technologies, Aurora, IL, USA). This handheld meter was pushed into the ground and automatically collected soil strength measurements every 2.5 cm increment with a built-in ultrasonic depth sensor. In each plot, the soil strength was measured three times before and after rolling treatments for both the center of the plot and on the wheel driving path.
Analysis of variance (ANOVA) was performed on termination rates and VMC using SAS software release 9.2 [
24]. Treatment means were separated by the Fisher’s protected LSD test at an α = 0.10 probability level. Where significant interactions between treatments and years occurred, or differences between years were significant, data were analyzed and presented separately; otherwise, data were combined.
4. Conclusions
Summer cover crops are an important component to effectively cover the soil surface to prevent soil erosion and runoff associated with high-intensity rainfall events. Results have shown that rolling twice or three times over the same cover crop area increased cover crop termination rates compared to rolling once. For iron clay peas, the termination rate averaged over the years and weeks was 51% for rolling once, 61% for rolling twice, and 72% for rolling three times. Similarly, the overall termination rates for pearl millet were 60%, 65% and 70% for rolling once, twice and three times, respectively. Compared with the control (non-rolled cover crops), rolling down and crimping resulted in increased soil volumetric soil moisture (VMC), indicating improved soil-water conservation for both cover crops due to rolling. During the 21-day evaluation period in the summer of 2016, a lack of rainfall and high average max temperatures (32.6 °C) created drought conditions that significantly reduced the volumetric soil moisture content on sandy loam soil planted with iron clay peas. This unusually dry period in 2016 also affected the biomass production of cover crops, especially pearl millet, generating significantly less biomass compared to 2017 (3733 kg ha−1 (31%)) and 2015 (5540 kg ha−1 (39%)). The soil strength for sandy loam planted with iron clay peas was assessed in 2015 and in 2017. No measurements were performed in 2016 due to severe drought preventing the hand compaction meter from moving down through the soil profile. The soil strength was not different for rolling treatments and among wheel traffic, center of plot and control at a 15–30 cm depth. At a 0–15 cm depth, the soil strength was below the 2.0 MPa threshold for root penetration resistance. Similarly, the soil strength for clay soil planted with pearl millet in 2015 and 2017 was lower than the 2.0 MPa threshold. In contrast, in 2016, the soil strength between positions and between rolling treatments was not different; however, the soil strength slightly exceeded 2.0 MPa for these parameters at a 0–15 cm depth due to unusually low soil volumetric moisture content related to drought conditions. Based on results from this experiment, summer cover crop termination rates vastly increased with rolling/crimping twice or three times over the same cover crop area compared with a single pass. Such findings are important for organic systems with cover crops, where only mechanical termination such as rolling/crimping can be utilized, as terminating cover crops with commercial herbicides is prohibited. Another important benefit from flattening and crimping cover crop against soil surface is conserving soil water through a mulching barrier, which resulted in higher volumetric soil moisture due to decreased soil water evaporation. Notably, rolling/crimping twice or three times over the same cover crop area did not cause soil compaction. Changes in soil strength were not affected by rolling treatments but depended on changes in soil moisture.