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Producing Grazeable Cover Crops During Summer Fallow in Winter Wheat

Producers in Oklahoma and surrounding states grow winter wheat in a continuous system, where the field is planted in the fall and harvested in late spring. Then the field is left summer fallow, when it is prone to soil erosion. A study conducted in the southern Great Plains, which includes Oklahoma, demonstrated soil losses from summer fallow fields increased 18 times when compared to fields cover cropped in summer (Sharpley & Halvorson, 1994). This huge soil loss decreased soil nitrogen by four times and phosphorus content by three times. Those nutrient losses might have contributed to wheat yield reduction in the region (Patrignani et al., 2014). These production losses are the sales pitch of conservationists, who typically follow with the arguments that cover crops also sup-press weeds and “improve soil health” with time. The latter is a generalized term used to synthesize increased soil water infiltration, holding capacity and nutrient retention. Although all those arguments are supported by several scientific works, most of them were performed in the southeastern U.S., where summer rainfall is higher and better distributed than in Oklahoma, making summer cover crops a success.

 

Nevertheless, dry summers are a frequent concern for Oklahoma producers who rely on any fast-cash summer crop or hay forage. Moreover, investing in summer cover crops becomes even more concerning because no financial gain is expected in the near future. It is all about preserving and improving soils for future profit. That’s why farmers will opt for low input summer cover crops and skip fertilization and herbicide application. Furthermore, producers may choose to graze cover crops to recuperate some seed and establishment costs. The option of grazing cover crops becomes even more attractive and, in some cases, a necessity when a summer drought period drastically reduces forage production of perennial pastures.  

 

The objective of this Fact Sheet is to discuss the potential of grazing summer cover crops and their effects on the fol-lowing winter wheat crop. All discussion is based on findings obtained from soil and weather conditions in Oklahoma and is focused on finding a middle ground between profitability and conservation. All findings and discussion mentioned in this Fact Sheet is a summary of Horn et al. (2020), which is an open-access article published in the Agronomy Journal.

 

The Study

The top three legumes and grasses asked about by Oklahoma producers in recent years were evaluated, along with two selected mixtures. A complete listing of cover crops, seeding rates and cultivars selected are provided in Table 1. The effect of these cover crops on the next winter wheat crop was compared to summer fallow fields (i.e., weeds controlled by regularly disking the soil at 4 inches every 15 days). Two tests were established in disked and cultipacked fields near Chickasha and Perkins in mid-June 2016 and 2017. No fertilizers or herbicides were applied at any time during the summer. The initial soil fertility and texture for both locations are presented in Table 2. All summer cover crops fields were split into three subfields in late July (six weeks after planting) and different simulated grazing managements were applied in each third of the fields. The simulated grazing management strategies were:

  • Severe – all cover crops were scalped (i.e., cut at a stubble height lower than 1 inch)
  • Recommended – legumes cut at 3 inches and grasses/mixtures cut at 6-inch stubble height
  • Ungrazed cover crop – plants were not cut

 

Cover crops were allowed to continuously grow until mid-September (14 weeks after planting), when they were chemically terminated by spraying 48 fluid ounces glyphosate per acre. The desiccated cover crops were kept standing for four weeks. Plots were fertilized with nitrogen (as urea) at 60 pounds of per acre and Gallagher hard red winter wheat was no-till planted into the standing cover crops at a seeding rate of 70 pounds per acre in mid-October at all locations. An additional 60 pounds per acre of nitrogen (as urea) was applied before wheat reached the Feekes 6 growth stage (jointing). At maturity in early June, wheat grain was harvested. No chemical weed control was performed during the winter wheat growing season to allow evaluation of the effect of cover crop soil cover on controlling weeds.

 

Table 1. Summer cover crops.

Cover crops Scientific name Cultivar Seeding rate (lbs/acre)
Forage soybeans Glycine Max KS 5004N 25
Cowpea Vigna unguiculata. Chinese Reds (CR) 20
Mung bean (MB) Vigna radiata Berkens (BE) 20
Pearl millet (PM) Pennisetum glaucum. K-Graze (KG) 15
Sorghum-sudangrass (SS) Sorghum bicolor ×    
  S. bicolor var. Sudanese AS6402 BMR 20
‘Triple Treat’ SS (TTSS)   Triple Treat (TT) 25
PM+MB   KG+BE 12+10
TTSS+CW   TT+CR 12.5+10

 

Table 2. Soil fertility and texture at six inches depth in Perkins and Chickasha before cover crops establishment in 2016.

Site pH TN
(%) 
Phosphorus (mg kg-1 Potassium (mg kg-1) OM
(%) 
Sand (%)   Silt  (%) Clay (%)
Perkins 6.3 0.07 225 1,244 1.01 49.4 35.0 15.6
Chickasha 6.0 0.15 260 1,495 1.57 27.5 48.0 24.4

TN: Total soil nitrogen

OM: Organic Matter

 

Outcome

  • Grazing to the ground did not always result in in-creased forage availability.

All cover crops produced acceptable amounts of forage in late July 2016. As expected, legumes produced less forage than grasses (Figures 2 and 3). Severe-simulated grazing resulted in higher forage availability than recommended. However, these higher forage availability in severe-simulated grazed covers varied from negligible (1%) to significant (33%) when compared to recommended-simulated grazed cover crops. The study indicates grazing to the soil surface provides a 33% increase in forage consumption at best. However, additional data in the coming years are needed to determine if this can be expected every year.

 

  • Grasses and mixtures are more effective than legumes in suppressing weeds and producing forage in mid-Summer.

In 2016, the total forage production (cover crop + weeds) of legumes was greater in Perkins than Chickasha (Figures 2 and 3). However, the greater legume forage yields found in Perkins werean artifact of a high incidence of weeds (29% to 51%) that inflated total forage yields. In fact, the actual legume forage yield was similar in both locations. These similarities in yields became apparent when the weed biomass was deducted from the total yields.

 

Different from legumes, the total grasses and mixtures forage yields produced in Chickasha were greater than in Perkins in 2016 (Figures 2 and 3). Also, the actual amount (i.e., weeds – deducted amount) of grasses and mixtures was much greater in Chickasha than in Perkins.

 

Good quality, weed-free forage mixtures were produced in Chickasha, 2016. However, the mixtures were 98% dominated by grasses and produced less forage than solely planted grasses. Thus, the evaluated mixtures were merely low-producing versions of the grasses. Similar mixture results were found at Perkins that year. Total forage production in mixtures was lesser than in grass cover crops and legume incidence in mixtures was low (5% to 13%). The only difference from Chickasha’s findings was that weed incidence in Perkins was much higher (18% to 33%).

 

Cover crop following timeline.

Figure 1. Cover crop following wheat timeline.

 

Forage production of tested cover crops in late July of 2016 in Chickasha.

Figure 2. Forage production of tested cover crops in late-July of 2016 in Chickasha.

 

Forage production of tested cover crops in late July of 2016 in Chickasha.

Figure 3. Forage production of tested cover crops in late July of 2016 in Chickasha.

 

Weeds

Volunteer crabgrass was the overwhelming weed observed in Perkins, 2016 (Figure 4). Although crabgrass was labeled as a weed, it is considered a good summer forage and provides good soil cover. Therefore, the crabgrass-infested cover crops in Perkins was suitable for grazing and cover production. To learn more about crabgrass as forage, see PSS-2790, Managing Crabgrass in a Continuous Graze out Wheat System and  CR-2606, Oklahoma Crabgrass Variety Performance Test. Although the weed pressure in Chickasha was much lower, pigweeds and stinkgrass were the dominant weeds (Figure 3B), both of which are undesirable as forage and soil cover.

 

High crabgrass infestation and moderate stinkgrass infestation in legumes cover crops at mid-July 2016 in Perkins and Chickasha.

Figure 4. High crabgrass infestation (A) and moderate stinkgrass infestation (B) in legumes cover crops at mid-July 2016 in Perkins and Chickasha, respectively.

 

Soil Fertility

As previously discussed, Perkins had higher weed incidence and lesser cover crop yields than Chickasha in 2016. The difference between locations is likely due to their contrasting soils. The soil type in the Chickasha fields is a clay loam soil with good initial fertility. On the other hand, the soil type in Perkins is a sandy loam soil with low initial fertility (Table 2). Perkins fields were not fertilized and resulted in poor cover crop performance in (Figure 5). Cover crops with improved genetic potential in producing forage and competing against weeds demand an adequate amount of nutrients to express their desirable traits. Their genetics alone will not do the trick. Fields in Perkins failed to provide a proper amount of nutrients to cover crops, making them low yielding and susceptible to weeds.

 

Sorghum-sudan forage production at late July 2016 at low-fertile soils, Perkins and fertile soils, Chickasha.

Figure 5. Sorghum-sudan forage production at late July 2016 at (A) low-fertile soils, Perkins and (B) fertile soils, Chickasha.

 

Rainfall

In mid-June 2017, no rainfall was observed for more than two weeks after replanting cover crops at the Perkins site. This prolonged dry period resulted in cover crop failure. In Chickasha, a few showers totaling 1.5 inches of rainfall a week after replanting allowed cover crop emergence in 2017, but no precipitation was observed for 29 days after emergence. Thus, the amount of forage was so limited that a high proliferation of weeds (25% to 89%) was observed (Figure 6); and only the severe-simulated grazing was possible due to small forage production at the end of July.

 

This second-year planting attempt demonstrated how erratic rainfall patterns are in Oklahoma. In 2016, precipitation was well-distributed throughout the whole summer, allowing the right growing conditions for cover crops most of the time. Conversely, extended drought conditions during June and July followed by short-duration, high-intensity rainfall during early August made the 2017 season challenging for cover crop production. The best approach for overcoming these unpredictable rainfall patterns could be the implementation of flexible planting dates. For instance, delaying the cover crop planting after an drought-ending rain could be a successful approach for the 2017 season.

 

Forage production of tested cover crops in late July 2017 in Chickasha.

Figure 6. Forage production of tested cover crops in late July 2017 in Chickasha.

 

Grazing

From late July to mid-September, cover crops were allowed to regrow in all locations and years. In 2016, recommended- and severe-simulated grazed cover crops had similar final soil to ungrazed cover crops at termination (mid-September). These results contradicted expectations. Common sense says cover crops could produce more soil cover if allowed to grow continuously without grazing. Instead, the ungrazed cover crops reached maturity weeks before termination and started to dry and leaves started to shatter. Simultaneously, recommended- and severe-simulated grazed cover crop were actively growing and matched ungrazed cover crops soil at termination. Figure 7 depicts how the simulated-grazed cover crops were able to regrow quickly during late summer 2016.

 

This incredible amount of cover crop regrowth was possible in 2016 because rainfall was abundant and well distributed after late July grazing. Nevertheless, it is fair to assume grazed cover crops could produce less soil cover than ungrazed if a prolonged drought period started in late July. Also, the recommended-grazed cover crops could have shown a slight regrowth advantage over severely grazed cover crops if rainfall was limited after grazing in 2016. Therefore, good management practices indicates to stop grazing at the 3-inch stubble height for legumes and the 6-inch stubble height for grasses.

 

Pearl millet cover crop regrowth at two weeks before termination in Chickasha, 2016.

Figure 7. Pearl millet cover crop regrowth at two weeks before termination in Chickasha, 2016.

 

Sorghums and Mixtures

In 2016, all cover crops at Perkins produced 2,000 pounds per acre of total soil cover (cover crops + weeds), except pearl millet, which only produced 1,250 pounds per acre. Although the total final soil cover was similar among most cover crops, the actual amount of cover crop varied. Sorghum and mixture soil cover were 30% dominated by weeds, and legumes soil cover was 60% dominated by weeds. Thus, pearl millet showed the least performance, where 80% of its total soil cover biomass was weeds.

 

Improved soil cover production was observed in Chickasha, 2016. Sorghums and mixtures produced the greatest amounts of total soil cover (3,500 pounds per acre), where 99% of the soil cover was dominated by sorghum plants. Pearl millet had intermediate total soil cover production (2,400 pounds per acre), with 98% of the total soil cover the actual cover crop. Finally, legumes produced the least total soil cover amount (890 pounds per acre). Mung bean and cowpea were 80% and 60%, respectively, dominated by the actual cover crop; conversely, forage soybean was 65% dominated by weeds.

 

In 2017, the total soil cover production of all cover crops was considered small in Chickasha (1,000 to 1,900 pounds per acre). Also, weed incidence was high in all cover crops at 40% in sorghums and mixtures; 60% in pearl millet, cowpea and mung beans; and 90% in forage soybean. This small and weed-infested soil cover production in 2017 was attributed to prolonged dry periods during summer.

 

High-biomass Cover Crops

Wheat protein content of fields previously producing a total of 5,000 pounds per acre of dry biomass (forage + soil cover) was similar to wheat fields following summer fallow. However, wheat grain quality started to decrease when cover crop total dry biomass production exceeded 5,000 pounds per acre. For every extra 1,000 pounds per acre of total dry biomass that exceeded 5,000 pounds per acre production, a reduction in wheat grain protein content was estimated at 0.2%. Moreover, wheat yields also were reduced when total dry biomass production exceeded 5,700 pounds per acre. In this case, for every extra 1,000 pounds per acre of total dry biomass that exceeded 5,700 pounds per acre production, a reduction was estimated at 2 bushels of wheat per acre. Furthermore, grasses and mixtures were the cover crops producing dry-biomass amounts higher than the 5,000 pounds per acre threshold. Conversely, legumes never achieved a total dry biomass production of 5,000 pounds per acre during the experiment; thus, grain production and quality of the following wheat was not reduced.

 

These findings revealed that opting for high-biomass-producing cover crops, such as pearl millet and sorghums, may hurt the following wheat grain production and quality. Producing high amounts of dry biomass during summer extracts considerable amounts of soil water and nutrients, such as nitrogen. Therefore, proper soil fertilization and faith in the weather are necessary when opting for a high-biomass-producing grass cover crop. Otherwise, opting for a drought-resistant, short-cycle legume cover crop may be desired. Consider that: 

  • Opting for a legume solves the problem of producing an excessive amount of biomass that will take a lot of water from the soil. Also, legumes have superior forage quality than grasses; therefore, good animal gains are possible with less forage production. Finally, legumes can fix nitrogen, decreasing fertilizer needs.
  • Opting for a short-cycle legume results in less soil water use during summer, allowing late summer rainfalls to replenish soils with water for the following wheat.
  • Opting for a drought-resistant, short-cycle legume further improves the system by adding resilience to it. In other words, drought-resistant legumes may not produce the highest biomass amounts. Still, they will guarantee forage and soil cover production if a prolonged summer drought strikes.

 

Wheat interseeded at cover crops at mid-Novem-ber in Chickasha, 2016.

 

 Figure 8. Wheat interseeded at cover crops at mid-November in Chickasha, 2016.

 

References

  • Horn, K.M., A.C. Rocateli, J.G. Warren, K.E. Turner, and J. A. Antonangelo. 2020. Introducing grazeable cover crop to the winter systems in Oklahoma. Agronomy Journal, 1-18. https://doi.org/10.1002/agj2.20326
  • Sharpley, A., & Halvorson, A. (1994). The management of soil phosphorus availability and its impact on surface. In R. Lal & B. A. Steward (Eds.), Soil processes and water quality (pp. 7–90). Boca Raton, FL: Lewis Publishers.
  • Patrignani,A., Lollato,R. P., Ochsner, T. E.,Godsey,C. B.,&Edwards,J. (2014). Yield gap and production gap of rainfed winter wheat inthe southern Great Plains. Agronomy Journal, 10 6(4), 1329–1339. https://doi.org/10.2134/agronj14.0011

 

Alex Rocateli

Forage Systems Extension Specialist

 

Jason Warren

Soil and Water Conservation Extension Specialist

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