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Article

Soybean Relative Maturity, Not Row Spacing, Affected Interseeded Cover Crops Biomass

Department of Plant Sciences, North Dakota State University, Fargo, ND 58104, USA
*
Author to whom correspondence should be addressed.
Submission received: 20 April 2021 / Revised: 10 May 2021 / Accepted: 11 May 2021 / Published: 13 May 2021
(This article belongs to the Special Issue Intercropping Systems for Sustainable Agriculture)

Abstract

:
Adoption of cover crop interseeding in the northwestern Corn Belt in the USA is limited due to inadequate fall moisture for establishment, short growing season, additional costs, and need for adapted winter-hardy species. This study evaluated three cover crop treatments—no cover crop, winter rye (Secale cereale L.), and winter camelina (Camelina sativa (L.) Crantz)—which were interseeded at the R6 soybean growth stage, using two different soybean (Glycine max (L.) Merr.) maturity groups (0.5 vs. 0.9) and two row spacings (30.5 vs. 61 cm). The objective was to evaluate these treatments on cover crop biomass, soil cover, plant density, and soybean yield. Spring wheat (Triticum aestivum L.) grain yield was also measured the following year. The early-maturing soybean cultivar (0.5 maturity) resulted in increased cover crop biomass and soil cover, with winter rye outperforming winter camelina. However, the early-maturing soybean yielded 2308 kg·ha−1, significantly less compared with the later maturing cultivar (2445 kg·ha−1). Narrow row spacing had higher soybean yield, but row spacing did not affect cover crop growth. Spring wheat should not follow winter rye if rye is terminated right before seeding the wheat. However, wheat planted after winter camelina was no different than when no cover crop was interseeded in soybean. Interseeding cover crops into established soybean is possible, however, cover crop biomass accumulation and soil cover are limited.

1. Introduction

In the northern crop growing areas in the USA, crop rotations were simplified, and corn (Zea mays L.) and soybean (Glycine max (L.) Merr.) became dominant crops. As a result, ecosystem services delivery, due to this shift in farming system, declined [1]. For instance, after harvest, a soybean field has limited cover [2] and may result in soil erosion, mainly by wind. Including cover crops in the cropping system provides soil cover, increases biodiversity and soil organic matter, utilizes available nutrients by preventing leaching, and may increase growth and yield of the following crop [3]. Overwintering cover crops that resume growth in the spring in the northwestern Corn Belt (NWCB) were proven to provide many ecological beneficial attributes. Benefits, however, depend on cover crops growth to cover the soil [4,5,6]. Cover crop adoption is steadily increasing in farming operations across the United States, especially in the eastern Corn Belt [7].
One factor affecting the integration of cover crops into an existing crop is additional costs. These additional costs lead to the common economic challenges for cover crops of how to demonstrate a measurable economic return [8,9]. Corn and soybean in the NWCB region are harvested at the end of September through October, and the first fall frost can be expected also by the end September or in October. Therefore, the opportunity to seed cover crops after the harvest of the main crop is limited to years with early harvest and a late fall killing frost. Alternative methods of seeding cover crops before the main crop is harvested are needed for a successful cover crop establishment and enough time to accumulate biomass and cover the soil.
Winter camelina (Camelina sativa (L.) Crantz) is an annual crop in the Brassicaceae family that has two distinct biotypes, spring and winter [10,11,12]. The interest in winter camelina as a cover crop increased since it is one of the few annual broadleaf cover crop that survives the winter in the NWCB and resumes growth in the spring [13,14,15,16].
Rye (Secale cereale L.) is the most used winter-hardy cover crop in the Midwest in the USA because it survives the winter, even when planted late in the growing season after the main crop harvest. In the spring, dormancy breaks, and rye resumes growth covering the soil before planting the following crop [3,17,18]. Rye minimum temperature for germination is 1 °C, and vegetative growth starts at 3 °C [9]. In addition, due to the fibrous rye root system and the ability to take nitrate up, nutrient leaching can be reduced. Use of winter rye is a cost-effective strategy to reduce nitrate and phosphorus loading to water sources [19]. However, only recently, producers in the most northern USA production region are considering incorporating winter rye into their farming system.
Interseeding of cover crops into soybean at different growth stages was reported [15,20,21,22]. By growing an early-maturing soybean, it may be possible to give the cover crops more time in the fall to establish and grow. In addition, wider soybean rows are expected to allow more of the sunlight to penetrate the canopy. Interseeding can be done by direct seeding in between the rows with specialized equipment or broadcasting the cover crop seed before the main crop matures. Seeding before the main crop is mature gives the cover crop some additional time to grow before the fall-killing frost [23]. Producers want to be assured there is no yield penalty to the main crop when interseeding cover crops into the main crop nor yield reduction of the spring sown crop after terminating the winter hardy cover crop [9]. No previous research evaluated a combination of soybean maturity and row spacing on the establishment of cover crops in the NWCB.
This study evaluated the effects on cover crops interseeded into soybean, using two different soybean maturity groups and two row spacings. The objective was to evaluate the effects of these treatments on cover crops’ (camelina and rye) biomass, soil cover, plant density, soybean yield, and subsequent wheat (Triticum aestivum L.) spring cover and grain yield.

2. Materials and Methods

2.1. Experimental Design and Treatments

A total of five experiments were conducted in North Dakota in 2017 and 2018 (Table 1). The experiments were conducted at an experimental site located at Fargo, ND (46.932124° N, 96.858941° W). One experiment at Fargo was planted on soil that was tile-drained in 2008 with sub-surface perforated polyethylene tile lines placed at 100 cm depth with 7.6 m between tiles. Tile is commonly used in the Corn Belt in the USA. The second experiment at Fargo did not have tile drainage. Both soils at Fargo were naturally poorly or very poorly drained. The parent material of the soil was clayey glaciolacustrine deposits [24].
The second location in 2017 was at Casselton, ND site (46.880049° N, 97.246534° W). The parent material of the soil was fine-silty glaciolacustrine deposits [24] (Table 1). Weather data for the 2017 and 2018 growing seasons were obtained from the North Dakota Agricultural Weather Network [25].
Each separate experiment at each location and year was defined as an ‘environment’. Each experiment had four replicates. Soil samples were taken at all sites just after the first killing frost in September. The soil is typically frozen from October to mid-April. Two soil samples, to depths of 0–15 cm and 15–61 cm, were taken at each sampling location. Soil samples were tested for NO3-N, Olsen P [26], K, pH, and organic matter (Table 2). Chemical fertilizer was not applied before or during the soybean growing season, as P and K soil test levels did not require fertilizer application. Soybean seed was inoculated to stimulate biological N2-fixation [27].
The experimental design was a randomized complete block design with a split-plot arrangement with the row spacing as main plot. Within each main plot, there was a randomized factorial combination of two soybean relative maturities and three cover crop treatments. Plot row spacings were narrow (30.5 cm) or wide (61 cm). Soybean relative maturities were early (0.5) or late (0.9) [28]. Cover crop treatments were no cover crop, winter camelina, and winter rye. The experimental unit size was 1.5 by 7.6 m.
In addition to the interseeding part of the study, eight plots within each replicate were used to represent growth of each cover crop after removing the soybean plants just before interseeding the cover crops to simulate cover crops growth without soybean competition for light, soil water, and nutrients. The treatments were designated as ‘Soy’ for plots without soybean biomass removed and ‘No-soy’ for plots with soybean biomass removed.
Narrow-row plots (30.5 cm row spacing) had four soybean rows seeded with a Hege 1000 no-till planter (Hege Company, Waldenberg, Germany). Wide-row plots were planted with the same planter at 61 cm row spacing. The seeding rate was 469,300 live seeds ha−1. The early-maturity soybean cultivar used was Asgrow brand “AG0536”, which has a relative maturity of 0.5, and for the late maturity, the cultivar was Asgrow ‘AG0934,’ which has a relative maturity of 0.9. They both are ‘Roundup Ready 2 Yield soybeans’ (glyphosate, N-(phosphonomethyl) glycine) (Bayer, St. Louis, MO, USA), with resistance to soybean cyst nematode (Heterodera glycines) and Phytophthora spp., and the seed was coated by the company with Acceleron (a.i. pyraclostrobin and metalaxyl) (Bayer, St. Louis, MO, USA) seed treatment. Both cultivars were inoculated with Vault SP (Bradyrhizobium japonicum) (BASF, Ludwigshafen, Germany) at a rate of 1.8 g·kg−1 soybean seed.
Four ‘No-soy’ plots were grown with the early-maturity soybean cultivar and four with the late-maturity cultivar. Upon reaching the R6 growth stage [29] in the early- and the late-maturing soybeans, plants were removed by a sickle-bar mower (Troy-bilt, Valley City, OH, USA), which cut soybean plants 3 cm above soil surface. Then, cover crops were seeded in the ‘No-soy’ and interseeded in the ‘Soy’ experimental units, when the soybean was in R6 stage of development; dates varied based on relative maturity of the cultivar, as indicated in Table 3. Winter rye cultivar ‘Rymin’ with a 1000 seed weight of 33 g was seeded at 67 kg live seeds ha−1. Winter camelina cultivar ‘Joelle’ with a 1000 seed weight of 1.1 g was seeded at 10 kg live seeds ha−1.
For wide-row plots, cover crops were planted in two parallel rows with a customized two-blade V-hoe spaced to make parallel furrows 15.3 cm apart. The parallel rows were planted in the two-center soybean rows. A single additional cover crop row was planted 15.3 cm from a soybean row, resulting in three cover crop rows in each experimental unit. For the narrow row spacing, a single furrow was made in the center between all soybean rows, 15.3 cm from each corresponding row, resulting in three cover crop rows. Furrows were made to the depths of 2.5 cm for rye and 1.3 cm for camelina.
Weeds in soybean were controlled during the vegetative growth stage using two applications of Roundup PowerMAX (a.i. 48.7% glyphosate, N-(phosphonomethyl) glycine (Bayer, St. Louis, MO, USA). The herbicide was applied using TeeJet AIXR 110015 nozzles (TeeJet Technologies, Springfield, IL, USA) at a rate of 1.6 L ha−1 in 94 L ha−1 water and a spray pressure of 200 kPa. Hand weeding was used when needed to control weed escapes. Disease and insect pressure were monitored throughout the season, and Mustang Max (a.i. 9.15% Zeta-cypermetrin*S-Cyano) (FMC Corporation, Philadelphia, PA, USA) foliar insecticide was used against soybean aphid (Aphis glycines Matsumura) at a rate of 292 mL ha−1.
Before seeding hard red spring wheat (HRSW), in the spring following soybean, cover crops were terminated using one application of Roundup PowerMAX as described previously.
In 2018, the HRSW cultivar ‘Glenn’ was used, and in 2019, the cultivar used was ‘SY Ingmar’. Spring wheat was planted in the two Fargo experiments in the springs of 2018 and 2019. Wheat was planted with a Great Plains 3P605NT no-till planter (Great Plains Ag, Salina, KS, USA) as soon as field conditions were favorable in early May, with seven rows spaced 18.3 cm apart using a seeding rate of 2,739,000 live seeds ha−1. Seeds were planted to a depth of approximately 2 cm. Nitrogen (N) was applied at a rate of 120 kg and 130 kg·ha−1 in 2018 and 2019, respectively.
Weeds were controlled with a foliar applied herbicide sprayed at 200 kPa using TeeJet 8001 XR nozzles (TeeJet Technologies, Springfield, IL, USA) using 94 L ha−1 water. In 2018, Wolverine Advanced (a.i 4.56% fenoxaprop-p-ethyl, 6.13% bromoxynil octanoate, 5.93% bromoxynil heptanoate, 1.5% pyrasulfotole) (Bayer, St. Louis, MO, USA) was used at a rate of 2 L ha−1. In 2019, Supremacy (a.i 36% fluroxypry, 4.5% thifensulfuron-methyl, 1.5% tribenuron) (Arysta LifeSciences, Cary, NC, USA) at a rate of 439 mL ha−1 and Axial XL (a.i. 5.05% pinoxaden) (Syngenta, Greensboro, NC, USA) at a rate of 1.2 L ha−1.
Soybean and wheat were harvested after physiological maturity [29,30] using a Wintersteiger Classic plot combine (Wintersteiger, Austria). Seeds were cleaned using a seed cleaner (Ferrell-Ross, Bluffton, IN, USA). Then, seed samples were weighed on a Mettler Toledo XS6001S scale (Mettler-Toledo, LLC, Columbus, OH, USA). Seed moisture and test weight were determined using a GAC 2100 moisture tester (DICKEY-John Corp., Minneapolis, MN, USA). Seed yield was corrected to 130 and 135 g·kg−1 moisture content for soybean and wheat, respectively.

2.2. Data Collection

Cover crop plants were counted within the center two rows of soybeans. Sampling areas were 50 cm × 30.5 cm for narrow row plots and 25 cm × 61 cm for wide row plots. Cover crop plants were counted in the fall after all rye and camelina plants emerged.
Soil green cover percentage was measured using the mobile phone application Canopeo (Oklahoma State University, Stillwater, OK, USA) before the first killing frost in the fall and before cover crop termination the following spring. Pictures uploaded into the Canopeo app were taken in the center of each plot at a height of 1 m, allowing 15 cm from the outside of the last soybean row [31].
Cover crop biomass was harvested both in the fall and the spring. In the fall, harvest was done before the first killing frost; in the following spring, it was done preceding cover crop termination. Biomass was sampled from an area of 1 m by 30 cm. Cover crop plants were cut at the base of plants nearest to soil. Samples were then placed in a dryer at a temperature of 40 °C. Samples were left in the dryer until constant weight was reached and were weighed.
Soil covered by spring wheat was measured using Canopeo during the tillering in mid-June (Table 3). Pictures used for soil green cover were taken in the center of each plot at a height of 1 m.

2.3. Statistical Analysis

Statistical analysis was conducted according to the experimental design. All dependent variables were analyzed with a mixed model (PROC MIXED) on SAS 9.4 [32]. Row spacing, cultivar, and cover crops were analyzed as fixed variables. For the analysis for cover crops traits, the data from the treatment without cover crop interseeded into soybean were removed.
Environment was a random variable in the model. Treatment means were separated using Fisher’s protected least significant difference (LSD) at a 5% level of significance. The LSDs were calculated for the combined analysis across environments.
Data from plots with soybean biomass removed, designated as ‘No-soy’, and without biomass removed, designated as ‘Soy’, were analyzed separately with a mixed model (PROC MIXED) on SAS 9.3, as described previously. No differences were observed between row spacings for ‘No-soy’ plots, and data were combined across row spacing for further analysis. Cultivar differences were also not available since soybean biomass was removed, eliminating the differences in soybean plant senescence differences.

3. Results and Discussion

3.1. Cover Crops Emergence

Emergence of cover crops varied greatly with location and year. The 2017 growing season consistently had below average monthly precipitation when compared with historical averages. The only month with above average precipitation was September, which is a critical month for cover crop growth before going dormant in the fall. The early-soybean maturity cover crop planting date in 2017 was 17 August at Casselton and 18 August at Fargo. Precipitation of 5.9 mm was received on 16 August, resulting in ideal conditions for the first planting dates at both locations. Following cover crop planting, no precipitation event greater than 2.5 mm occurred until 15 September. This resulted in no germination of the second cover crop planting date until 20 and 21 September (Table 4).
Since no precipitation was received for over a month, early-planted cover crops struggled to survive. High crop residue from soybean leaf senescence also greatly inhibited the growth of the early-planted cover crops, as it smothered the plants. Once the plants were smothered, the drought stress was compounded and resulted in retarded growth or cover crop plant death. Peterson et al. [20] stated that rapid soybean leaf senescence can also stress winter camelina plants, as cover crop plants can acclimate to low light conditions of less than 20% photosynthetically active radiation (PAR) under the canopy, and with rapid leaf drop, cover crop plants were not able to adapt to higher solar radiation. The late-planted cover crops emerged following soybean senescence and were able to germinate through the crop residue.
The 2018 growing season had above average rainfall following both cover crop planting dates, resulting in more developed cover crops during soybean senescence. This allowed the cover crops to handle the substantial amount of soybean residue produced during senescence compared with the 2017 growing season.
Monthly average air temperatures were 4 °C and 2.4 °C higher in the months of May and June in 2018 compared with the historical average, providing the soybean crop a good start to the season (Table 4).
During the late-planting date in 2017 and both planting dates in 2018, soybean senescence coincided with cover crop emergence. Soybean leaves completely covered the small seedlings of camelina. The rye was able to emerge from soybean leaf residue quickly due to rapid leaf growth and height of the plant compared with the prostrate rosette leaf arrangement produced from winter camelina.

3.1.1. Presence and Absence of Soybean

The analysis of variance indicated that conditions (‘Soy’ and ‘No-Soy) and cover crop main effects were significant for all metrics except spring biomass (Table 5). Only significant effects in the analysis of variance are discussed herein. Significant interactions between a fixed and a random effect (environment) are not discussed.
Although removal of soybean plants resulted in higher soil cover and biomass compared with the ‘Soy’ treatment in the fall, the cover crops spring biomass from the ‘No-soy’ plots was 77% of the biomass recorded in the ‘No-soy’ plots in the fall (Table 6). The lower amount of biomass in the spring can be attributed to winterkill. Winter camelina loses the ability to survive the winter if it produces a relatively high amount of biomass or is seeded before 15 September in the fall [16].
‘No-soy’ plots were designed to simulate an environment for cover crop growth without light, nutrient, or water competition from soybean plants. The interseeded cover crops at the R6 growth stage of soybean were competing with fully established soybean plants for sunlight. This resulted in reduced cover crop stand and growth established in the fall compared to cover crops grown without soybean.

3.1.2. Cover Crops Fall and Spring Coverage and Biomass in Treatments with No Soybean (‘No-Soy’)

Winter camelina had lower cover percent and biomass compared with rye in both the fall and the spring (Table 7). Winter camelina had a slower establishment period, which set the plant behind compared with rye. Rye had higher soil coverage and biomass compared with camelina biomass, as was also reported in other research [15,20,21]. while winter camelina had more plants compared with rye. Rye produced only some tillers in the fall. and camelina stayed in the rosette stage and had limited foliar growth.

3.2. Cover Crops Soil Green Cover and Biomass in Treatments Interseeded into Soybean

The analysis of variance indicated that the soybean yield was significantly different for row spacing, but none of the cover crop metrics were significantly different (Table 8). The differences in soybean maturity and cover crop type resulted in significant observed differences.
The experiment was set up to investigate if there were any interactions between main factors, however, the ANOVA indicated that there was no interaction between soybean row spacing and cover crops, soybean maturity and cover crops, or the three way interaction of soybean row spacing by maturity by cover crops for any of the measured observations.
Only significant effects in the analysis of variance are discussed herein. Significant interactions between a fixed and a random effect (environment) are not discussed.

3.2.1. Row Spacing Effect

Narrow-row spacing produced higher soybean yield compared with wide-row spacing (Table 9). Previous research in the NWCB also reported higher soybean yields with narrow-row spacing [33,34]. This soybean yield difference may be due to the decreased total light absorption by the soybean plants in wider rows and/or competition for nutrients and water with higher plant density within rows in wider rows.
Based on this research, narrow row-soybean planting is recommended since cover crop differences were non-significant between row spacings. This difference of 180 kg·ha−1 higher yield in narrower rows results in a net income gain of $52.9 ha−1 when using a soybean price of $0.29 kg−1 when comparing 30.5 cm with 61 cm row spacing. The net loss for wider rows would be difficult to justify since the cover crop biomass production was not different at either row spacing (Table 9).

3.2.2. Relative Maturity of Cultivars Effects

Where the cover crop was interseeded earlier (in the early maturing cultivar), fall and spring cover crop soil cover percentages were higher, as were fall biomass, spring biomass, and stand counts (Table 10).
The later maturing soybean cultivar (0.9 vs. 0.5 maturity group) produced significantly higher soybean yields with an average difference of 137 kg·ha−1 relative to the earlier maturity soybean (Table 10). In other studies, higher yields for later maturing soybean cultivars in US soybean growing regions, including North Dakota, were also reported [34,35]. The difference of 137 kg·ha−1 in this study resulted in a per hectare reduced income of $42.26 ha−1 when using $0.294 kg−1 soybean price when the earlier maturing cultivar was used compared with the later maturing cultivar.

3.2.3. Cover Crop Effect

Biomass produced by winter rye at all times (fall 2017 and 2018 and spring 2018 and 2019) was significantly higher compared with that of winter camelina. There were significantly more established camelina plants in the fall compared to winter rye. This is most likely a function of seeding rate (Table 11).
These differences are consistent with ‘No-soy’ cover crop differences (Table 6). Spring soil cover in this study was similar to other studies for winter rye and camelina [15,19,20]. Another study suggested at least 30% of the soil surface should be covered to protect the soil from water and wind erosion [36]. There was not a significant difference in soybean yield when winter rye or camelina were interseeded.

3.3. Wheat Yield

Growing rye before planting wheat resulted in reductions in HRSW soil coverage and grain yield (Table 12). These differences were visually obvious and statistically significant, consistent with other research [20,37], with rye reducing wheat canopy cover by almost 20% (51.1 vs. 41.0%) and yield by 277 kg·ha−1 compared with wheat without previous cover crop (Table 12). When the overwintering winter rye resumed growth in the spring, the rye utilized nutrients and water, reducing the amount of available water for the subsequent spring wheat crop, which impacted development. It was reported that winter rye produces allelopathic compounds, which can affect wheat and other grasses growth [38], can carryover root diseases [39], and can immobilize N, which can negatively impact yield [40,41]. Wheat soil cover and wheat grain yield were similar after camelina compared with wheat after no cover crop in the soybean. This research shows that cover crops can be established in soybean and that there can be a negative effect on the subsequent crop. We terminated the cover crop at the same time as seeding wheat.
Future research could look at alternative termination methods and timings to reduce the negative effect of over-wintering rye on the following wheat crop. The other angle for additional research would be to evaluate other subsequent crops after interseeding rye into soybean, for instance, with flax (Linum usitatissimum L.) or forage crops.

4. Conclusions

Winter rye or camelina interseeded in an early-maturing soybean (0.5) had higher biomass yield and soil green cover compared with the same crops interseeded in a later maturing (0.9) soybean. However, the yield penalty of planting an early-maturity soybean cultivar was higher in value than the value of increased cover crop growth and cover. The value of the soybean yield reduction (137 kg·ha−1 × market price) between the two cultivars was significant. Based on the results of this study, planting an early-maturity soybean cultivar to allow more growth of interseeded cover crops is not recommended, as the loss of revenue is not compensated by an increase in cover crop biomass. In order to find out if long-term economic benefits from interseeding cover crops offset the yield reduction due to the utilization of an early-maturity cultivar, additional research is needed.
There was no significant difference in fall or spring biomass production with wide row spacing compared with the narrow row spacing. Thus, it is recommended to plant soybean in narrow row spacing (30.5 cm compared with 61 cm), as soybean yields were significantly higher with the narrower row spacing than wide row spacing. No soybean yield reduction was observed after the interseeding of the cover crops compared with soybean with no interseeded cover crop. This proves competition of cover crops with soybean plants when cover crops are seeded at the R6 growth stage of the soybean cultivars was negligible and that no economic soybean yield loss should be expected.
Seeding wheat on the same day as rye termination is not recommended. Winter rye reduced growth and grain yield of wheat. Our research indicates that there is an opportunity to establish winter rye by interseeding into soybean, but termination and subsequent crops selected need further investigation. Oppositely, interseeding winter camelina into soybean had no negative effects on wheat growth and yield. Thus, winter camelina can be utilized as a cover crop interseeded into soybean to follow a wheat crop the next growing season. However, biomass production and soil cover by camelina are probably not enough to keep the soil from blowing away. Future research should investigate if there is an economic benefit of adding camelina as a cover crop into soybean.

Author Contributions

H.J.K.: conceptualization, investigation, supervision, writing—review & editing. D.P.S.: writing—review & editing. K.L.J.: formal analysis, investigation, methodology, writing—original draft. M.T.B.: formal analysis, funding acquisition, investigation, project administration, resources, writing—review & editing. All authors have read and agreed to the published version of the manuscript.

Funding

This project was funded by USDA-NIFA, Award no. 2016-69004-24784.

Data Availability Statement

Raw data is available upon request to H. Kandel. Data has not been archived in a repository.

Acknowledgments

The authors would like to thank Chad Deplazes and Darin Eisinger for their technical assistance.

Conflicts of Interest

The authors declare no conflict of interest.

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Table 1. Soil series, soil taxonomy, and slope at Fargo and Casselton, ND.
Table 1. Soil series, soil taxonomy, and slope at Fargo and Casselton, ND.
LocationSoil Series Taxonomic Class Slope (%)
FargoFargoFine, smectitic, frigid Typic Epiaquerts0–1
and RyanFine, smectitic, frigid Typic Natraquerts
CasseltonKindredFine-silty, mixed, superactive, frigid Typic Endoaquolls0–2
and BeardenFine-silty, mixed, superactive, frigid Aeric Calciaquolls
Soil data obtained from [24].
Table 2. Soil test results before seeding soybean at all environments in 2017 and 2018.
Table 2. Soil test results before seeding soybean at all environments in 2017 and 2018.
YearLocationSampling DepthNO3-NP KpHOM
cmkg·ha−1mg·kg−1 g·kg−1
2017Fargo0–158154407.955
15–61763308.036
2017Fargo tile drained 0–155164327.955
15–61562908.235
2017Casselton0–1530393137.743
15–61104312907.936
2018Fargo0–151993307.856
15–617942868.136
2018Fargo tile drained0–1520133767.856
15–618673388.040
P based on the Olsen sodium bicarbonate extraction method, recommended for North Dakota soils [26], OM = organic matter.
Table 3. Dates of important measurements and field operations at Fargo and Casselton, ND in 2017, 2018, and 2019.
Table 3. Dates of important measurements and field operations at Fargo and Casselton, ND in 2017, 2018, and 2019.
Measurement/OperationFargoCasseltonFargo
201720172018
Soybean planting8 May10 May14 May
First herbicide application12 June12 June13 June
Second herbicide application7 July7 July2 July
Insecticide application25 August25 August12 July, 11 August
Early maturity soybean cover crop interseeding18 August17 August8 August
Later maturity soybean cover crop interseeding24 August24 August22 August
Cover crop emergence in early maturity soybean 23 August22 August28 August
Cover cop emergence in later maturity soybean 20 September21 September 3 September
Cover crop Canopeo measurements31 October3 November21 October
Cover crop biomass sampling1 November2 November22 October
Cover crop stand counts13 October12 October22 October
Soybean harvest 6 October4 October18 September
201820182019
Spring cover crop Canopeo12 May13 May12 May
Spring cover crop biomass sampling12 May13 May12 May
Spring wheat planting16 May- 31 May
Spring wheat Canopeo13 June-16 June
Spring wheat herbicide application13 June-2 July
Wheat harvest17 August-6 September
Canopeo = tool for calculating soil green cover percentage. No wheat was planted at Casselton in 2018.
Table 4. Monthly total precipitation, average air temperature, and historical data at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 4. Monthly total precipitation, average air temperature, and historical data at Fargo and Casselton, ND, 2017, 2018, and 2019.
FargoCasselton
Month201720182019Historical 2017 Historical
mm°Cmm°Cmm°Cmm°Cmm°Cmm°C
April257.661.7254.0356.8176.6376.3
May2614.04418.0708.67114.01713.27713.4
June5719.812321.48316.39919.08819.110018.7
July2322.38121.712121.37121.65021.28821.3
August5819.310120.69019.36520.75318.16720.4
September7016.56415.010716.66515.115215.36614.8
October208.7584.4887.9557.577.5627.3
Total280-477-584-461-366-496-
Historical data represent a 30 year average 1981–2010 [25].
Table 5. Mean squares for two soybean conditions (‘Soy’ and ‘No-Soy’) and two cover crops (CC) in five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 5. Mean squares for two soybean conditions (‘Soy’ and ‘No-Soy’) and two cover crops (CC) in five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
SOV dfFall Soil CoverSpring Soil CoverFall BiomassSpring BiomassFall CC Stand Count
2017–20182018–20192017–20182018–20192017–2018
%%kg·ha−1kg·ha−1Plants m−2
Env40.2160.1282015.1 *3798.5 *2514
Rep(env)150.069 *0.068 *178.4 *48.11484 *
Cond.12.187 *1.930 *3986.2 *812.159,245 *
Env × Cond.40.0530.029312.1511.3437
CC10.947 *0.539 *2353.9 *1584.5 *31,972 *
Env × CC40.0590.063164.0145.9385
Cond. × CC10.0980.0374.861.811,846
Env × Cond. × CC40.0220.021137.2 *112.7 *1408 *
Residual 460.0110.01132.845.5345
SOV = sources of variation. Cond. = soybean conditions (‘Soy’ and ‘No-Soy’), CC = cover crops (winter rye and camelina), Env = environment. * = significant at (p ≤ 0.05).
Table 6. Mean fall and spring cover crop soil green cover, biomass, and stand count in treatments with and without soybean averaged across row spacing and maturity across five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 6. Mean fall and spring cover crop soil green cover, biomass, and stand count in treatments with and without soybean averaged across row spacing and maturity across five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
TreatmentFall Soil CoverSpring Soil CoverFall BiomassSpring BiomassFall Stand Counts
2017–20182018–20192017–20182018–20192017–2018
%%kg·ha−1kg·ha−1plants m−2
‘Soy’8.1b 14.0b158b202a75b
‘No-soy’ 24.7a29.6a410a316a167a
Means followed by a different small case letter within a column are different at p ≤ 0.05. Experimental units had soybean biomass removed at the time of cover crop seeding.
Table 7. Mean fall and spring cover crop soil cover, cover crop biomass. and cover crop stand counts for two cover crops averaged across conditions and environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 7. Mean fall and spring cover crop soil cover, cover crop biomass. and cover crop stand counts for two cover crops averaged across conditions and environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Cover CropFall Soil CoverSpring Soil CoverFall BiomassSpring BiomassFall Stand Counts
2017–20182018–20192017–20182018–20192018
%%kg·ha−1kg·ha−1plants m−2
Winter camelina10.9b 17.7b315b223b154a
Winter rye21.8a25.9a505a410a89b
Means with a different small case letters within a column are different at p ≤ 0.05.
Table 8. Mean square values for row spacing (RS), maturity (Mat), cover crop (CC), and five environments (Env) at Fargo, ND, 2017, 2018.
Table 8. Mean square values for row spacing (RS), maturity (Mat), cover crop (CC), and five environments (Env) at Fargo, ND, 2017, 2018.
SOV dfCC Fall Soil CoverCC Spring Soil CoverCC Fall BiomassCC Spring BiomassFall CC StandSoybean YielddfWheat YieldWheat Soil Cover
2017–20182018–20192017–20182018–20192017–20182017–2018 2018–20192018–2019
%%kg·ha−1kg·ha−1plants m−2kg·ha−1 kg·ha−1%
Env40.03230.0223633.7820.3 *5646,531,173 *322,543,640 *0.4332
Rep(env)150.0149 *0.0218 *57.8 *57.8 *736598,695 *12665,821 *0.1535
RS10.01010.000428.437.7521,983,581 *11,241,3650.0984
Env × RS40.00310.002810.426.879205,5223312,5420.0087
Mat10.1461 *0.3152 *199.564.1 *7886 *1,131,392 *11,312,5280.5355
Env × Mat40.00970.008158.07.71208707310,1540.0153
CC10.2191 *0.1503 *1055.7 *505.8 *2540 *57,9632857,852 *0.4897 *
Env × CC40.0488 *0.0643 *260.3 *97.5 *912 *237,473656,851 *0.1141 *
RS × CC10.00240.00154.52.53457,708266,5630.0089
Env × RS × CC40.00150.00174.05.396109,7736141,5230.0101
RS × Mat10.00240.004310.629.62462115950.0055
Env × RS × Mat40.00140.004910.749.515255,564374,8520.0098
CC × Mat10.04840.034795.678.9218621,5452565,6240.4685
Env × CC × Mat150.00480.00746.88.1491 *148,2956132,4560.0145
RS × Mat × CC10.00250.001628.425.713921,513232,5240.0075
Env × RS × Mat × CC80.0064 *0.006831.2 *18.4341180,5056198,5550.0135
Residual Error900.00310.006013.316.1215149,295133178,3250.0098
SOV = sources of variation; df = degrees of freedom CC = rye and camelina. The df for wheat yield and wheat soil cover are different because only four environments had wheat, and to the cover crops, a no cover crop treatment was added to the analysis * = significant at p ≤ 0.05.
Table 9. Soybean seed yield, fall and spring cover crop soil green cover, cover crop biomass, and cover crop stand count readings for two row spacings averaged across cover crops and relative maturity across five environments planted at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 9. Soybean seed yield, fall and spring cover crop soil green cover, cover crop biomass, and cover crop stand count readings for two row spacings averaged across cover crops and relative maturity across five environments planted at Fargo and Casselton, ND, 2017, 2018, and 2019.
Row SpacingSoybean Yield
2017–2018
Fall Soil Cover
2017–2018
Spring Soil Cover
2018–2019
Fall Biomass
2017–2018
Spring Biomass
2018–2019
Fall Stand Count
2017–2018
kg·ha−1%%kg·ha−1kg·ha−1plants m−2
Wide (61 cm)2287b 8.914.117122079
Narrow (30.5 cm)2467a7.313.914118481
Means with different letters are different at p ≤ 0.05. If letters are absent, they are not significantly different.
Table 10. Soybean yield, fall and spring cover crop canopy coverage, cover crop biomass, and cover crop stand count readings for two cultivars averaged across five environments in Fargo and Casselton, ND, from 2017, 2018, and 2019.
Table 10. Soybean yield, fall and spring cover crop canopy coverage, cover crop biomass, and cover crop stand count readings for two cultivars averaged across five environments in Fargo and Casselton, ND, from 2017, 2018, and 2019.
CultivarSoybean Yield
2017–2018
Fall Soil Cover
2017–2018
Spring Soil Cover
2018–2019
Fall biomass
2017–2018
Spring Biomass
2018–2019
Fall Stand Count
2017–2018
kg·ha−1%%kg·ha−1kg·ha−1plants m−2
Early maturing (AG0536)2308b 11.1a18.4a193a226a98a
Late maturing (AG0934)2445a5.0b9.6b118b180b52b
Means followed by a different letter within a column are significantly different at p ≤ 0.05.
Table 11. Mean fall and spring cover crop soil coverage, cover crop biomass, and cover crop stand count readings for two cover crops averaged across five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Table 11. Mean fall and spring cover crop soil coverage, cover crop biomass, and cover crop stand count readings for two cover crops averaged across five environments at Fargo and Casselton, ND, 2017, 2018, and 2019.
Cover CropFall Soil Cover
2017–2018
Spring Soil Cover
2018–2019
Soybean Yield
2017–2018
Fall Biomass
2017–2018
Spring Biomass
2018–2019
Fall Stand Count
2017–2018
%%kg·ha−1kg·ha−1kg·ha−1plants m−2
Winter rye11.8a 17.1a2367242a259a62b
Winter camelina4.4b11.0 b241172b144b89a
Means followed by a different letter within a column are significantly different at p ≤ 0.05.
Table 12. Mean soybean yield for two cover crops averaged across five environments in Fargo and Casselton, ND, 2017 and 2018, and mean wheat soil cover and yield across four environments in Fargo, ND, 2018 and 2019.
Table 12. Mean soybean yield for two cover crops averaged across five environments in Fargo and Casselton, ND, 2017 and 2018, and mean wheat soil cover and yield across four environments in Fargo, ND, 2018 and 2019.
CultivarWheat Soil Cover
2018–2019
Soybean Yield
2017–2018
Wheat Grain Yield
2018–2019
%kg·ha−1kg·ha−1
Winter rye41.0b 23672534b
Winter camelina52.3a24112783a
No cover crop51.1a23682811a
Means followed by a different letter within a column are significantly different at p ≤ 0.05.
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Kandel, H.J.; Samarappuli, D.P.; Johnson, K.L.; Berti, M.T. Soybean Relative Maturity, Not Row Spacing, Affected Interseeded Cover Crops Biomass. Agriculture 2021, 11, 441. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11050441

AMA Style

Kandel HJ, Samarappuli DP, Johnson KL, Berti MT. Soybean Relative Maturity, Not Row Spacing, Affected Interseeded Cover Crops Biomass. Agriculture. 2021; 11(5):441. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11050441

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Kandel, Hans J., Dulan P. Samarappuli, Kory L. Johnson, and Marisol T. Berti. 2021. "Soybean Relative Maturity, Not Row Spacing, Affected Interseeded Cover Crops Biomass" Agriculture 11, no. 5: 441. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11050441

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