How Do Cover Crops Designed for Game Birds Affect Soil Health?

September 11, 2025

How Do Cover Crops Designed for Game Birds Affect Soil Health?

By Katja Koehler-Cole - Extension Educator, Nathan Pflueger - Precision Ag Coordinator, Pheasants Forever and Quail Forever

Sorghum plants dominate a tall cover crop mix in August 2024.

Who knew habitat acres could pay off twice? Wildlife-friendly cover crops improved soil health indicators in months. Learn how four Nebraska farmers made it happen. 


Key Takeaways
  • Full-season cover crops can improve soil health characteristics in the short term.

  • Providing game bird habitat and soil conservation can go hand in hand.


Introduction

In seed corn fields, pivot corners and isolation acres (areas to prevent cross pollination) are often planted to soybean. These areas could also be used to accomplish conservation goals, such as providing wildlife habitat. To this end, Pheasants Forever's Full Season Cover Crop Practices program pays producers to plant a specially designed cover crop in these acres. 

The cover crops must be in the field from June 1 to March 15 the following year, providing cover and forage resources for pheasants, turkeys and other game bird species. 

With the potential benefits of adding plant diversity and living roots, we wanted to explore whether these cover crops intended for game birds could also improve soil health characteristics. What we found was somewhat surprising. We often hear that soil health improvements with cover crops take a long time; however, we saw increases in soil organic carbon and biological activity in just 10 months. 

The following article describes how we conducted the study and what producers can take away from it.

How Was the Study Conducted?

Four seed corn farmers in central Nebraska participated in this study. They planted a 10-species cover crop mix* at a seeding rate of 28 lb/ac into pivot corners and isolation areas of their seed corn fields. 

Cover crops established well and grew to about 5 feet tall by August 2024. They were winter-killed, and residue remained standing until late March or April of 2025, when it was tilled into the soil.

Soil samples were collected on June 6, 2024, Aug. 22, 2024, and April 9, 2025, from cover-cropped and seed corn areas on each of the four farms participating in the study. For more information on the management of each farm, consult Table 1. 

At each sampling time, four soil samples were taken in the cover crop and four in the seed corn, with each sample consisting of 10 soil cores taken to a depth of 8 inches. Soil samples were analyzed for soil nitrate and two soil health indicators, and results were statistically evaluated.** 

*The cover crop mix consisted of dwarf forage sorghum, cereal rye, grain sorghum, buckwheat, flax, sunflower, forage radish, cowpeas, mung beans, and hairy vetch, seeded at 28 lb/ac.

**Results were statistically evaluated with SAS9.4 as a repeated measures analysis with a significance level of 0.1. Treatment (cover crop or seed corn) and time (June, August and April) were fixed effects and time nested within farm were random effects.

 

Soil Nitrate

Nitrogen (N), whether applied as fertilizer or inherent in the soil, is transformed by soil microbes into nitrate or ammonium before crops can use it. Nitrate is soluble in water whereas ammonium is not, making nitrate susceptible to run-off and leaching during rainfall or irrigation. Did cover crops decrease soil nitrate levels compared to seed corn acres?

The data shows large variations in soil nitrate concentrations throughout the year (see Figure 1), but whether that is due to the cover crop or differences in N fertilization is not clear.

Bar chart comparing soil nitrate levels in cover crop vs. seed corn fields at three sampling times, with overlapping error bars.
Figure 1. Soil nitrate concentrations under the cover crop (blue bars) and under seed corn (red bars). The lines on top of the bars are the standard error of the mean. Where standard errors overlap, the nitrate concentrations are not statistically different. Cover crops were planted in late May to early June and died with the onset of freezing temperatures in the fall. Cover crop residue remained in the field until late March or April.

In June, soil nitrate concentrations in seed corn were considerably higher than in cover crops, reflecting the application of N fertilizer in seed corn fields (Table 1). Between June and August, seed corn and cover crops took up more than half the soil nitrate. The cover crop mix included heavy N feeders such as sorghum (Figures 2 and 3).

By April, nitrate concentrations were similar between the cover crop and seed corn areas, likely due to N being released from decomposing seed corn and cover crop residue, as well as N fertilization on some farms between October and April.

Sorghum plants dominate a tall cover crop mix in August 2024.
Figure 2. Sorghum is predominant in the cover crop mix; picture taken in August 2024. (Nebraska Extension photo)
Diverse flowering cover crop mix with tall sunflowers at peak growth in August 2024.
Figure 3. The cover crop at its peak in August 2024. Many species including sunflowers were flowering. (Nebraska Extension photo)

Soil Organic Carbon

Soil organic carbon is probably the most well-known indicator of soil health. It makes up about 58% of soil organic matter and is the main source of energy for soil microorganisms. Soils with more organic carbon can support more microbes, leading to better nutrient cycling, soil aggregation, water infiltration and other benefits. 

Considering that plants add organic matter to the soil — in the form of residue and root exudates — does soil organic carbon increase under a full-season cover crop compared to seed corn fields?

To explain the data, it makes most sense to look at soil organic carbon’s interaction with the sampling time. Soil organic carbon under the cover crop was similar at each sampling time, averaging 1.76% which is equivalent to about 3.03% of total organic matter (see Figure 4). Under seed corn, soil organic carbon varied with the highest level measured in June at 1.89% (equivalent to 3.26% organic matter). 

When comparing the cover crop to seed corn, soil organic carbon under the cover crop was higher than under seed corn in August, but not at the other sampling times. Carbon inputs into the soil from vegetation were likely higher in August because the cover crops were growing actively. 

Bar chart comparing soil organic carbon in cover crop vs. seed corn fields at three sampling times, showing higher levels in August cover crops.
Figure 4. Soil organic carbon under the cover crop (blue bars) and under seed corn (red bars). The lines on top of the bars are the standard error of the mean. Where standard errors overlap, the organic carbon concentrations are not statistically different. Cover crops were planted in late May to early June and died with the onset of freezing temperatures in the fall. Cover crop residue remained in the field until late March or April.

Soil Respiration

As soil microbes feed on organic matter and reproduce, they respire CO2 just like other organisms. Measuring the amount of CO2 in a test called potential carbon mineralization (or soil respiration) can indicate the numbers and activity of soil microorganisms, which in turn can be a sign of how quickly residue breaks down and cycles nutrients back into the soil for crops to take up. Increasing the amount of microbial food sources — such as plant residue or root exudates released by actively growing plants — can lead to greater respiration. Temperature and moisture are also important factors in microbial growth, with soil respiration typically higher during the summer.

Did soil respiration increase due to the cover crop, time of sampling, or both? The answer is more complicated. The cover crop itself has an effect only when viewed in the context of its interaction with sampling time (see Figure 5). At the June sampling, respiration was lower under the cover crop than under seed corn. Actively growing seed corn provided a better food source and had more soil moisture than the cover crop, which was non-irrigated and where plants were still fairly small. 

By August, soil respiration was higher under cover crops than under seed corn, reflecting better conditions for microbes. Soil organic carbon and soil respiration levels follow the same pattern, illustrating the interdependence of microorganisms on their food source.

Bar chart of soil respiration in cover crop vs. seed corn fields, showing microbial activity differences at three sampling times.
Figure 5. Soil respiration (given as CO2 concentrations) under the cover crop (blue bars) and under seed corn (red bars). The lines on top of the bars are the standard error of the mean. Where standard errors overlap, the carbon respiration levels are not statistically different. Cover crops were planted in late May to early June and died with the onset of freezing temperatures in the fall. Cover crop residue remained in the field until late March or April.

Take-Home Message

A full-season cover crop designed for game birds shows promise to improve two important soil health characteristics — organic carbon and soil respiration — in the short-term. This could increase nutrient cycling, water infiltration, soil fertility and yields of subsequent crops. Follow-up studies are needed to verify long-term effects. If these soil health improvements lead to greater crop yields or reduced input costs, the full-season cover crop practice could become more appealing to farmers, especially if combined with the per acre payments or revenue from game bird hunting. 

Acknowledgements

The authors would like to thank the farmers for their willingness to participate in this study. Funding sources include Nebraska Extension, USDA Natural Resources Conservation Service (NRCS), the Nebraska Environmental Trust, Syngenta, Nebraska Game and Parks, and the National Fish and Wildlife Foundation.

Table 1. Management of seed corn and full-season cover crop fields on the four farms participating in this study.

Management

County Locations of Farms

Seward

York 1

Polk

York 2

Seed Corn Acres

Seed corn plantingMay 15, 2024April 23, 2024June 6, 2024June 10, 2024
N applied April-August 2024

4 gallons of 6-24-6 as starter

110 lb/ac

 

120 lb/ac100 lb/ac105 lb/ac
Short-season cover crop -

Turnips and radish, planted  July 2024*,

grazed

Cereal rye, planted September 2024Turnips and radish, planted  July 2024*, grazed
Seed corn harvestSept. 20, 2024Aug. 22, 2024Oct. 1, 2024Sept. 10, 2024
N applied October 2024 to April 2025150 lb/ac120 lb/ac--
Tillage----

Full-Season Cover Crop Acres

Full season cover crop plantingJune 6, 2024June 6, 2024June 12, 2024May 28, 2024
N applied April-August----
N applied October 2024 to April 2025150 lb/ac120 lb/ac--
TillageApril 4, 2025April 1, 2025April 1, 2025-

*planted when male rows are destroyed into remaining seed corn rows. Radish and turnips winterkill.

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