Scavenging and recycling deep soil nitrogen using cover crops on mid-Atlantic, USA farms
•Cover crops reduced nitrate in the upper 60–120 cm soil depths in the fall.•Winter cereal monoculture covers resulted in low spring topsoil and subsoil nitrate.•Covers with radish or legume resulted in low subsoil but high topsoil nitrate.•Winter cereal monoculture covers immobilized N and restrain...
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Published in | Agriculture, ecosystems & environment Vol. 309; p. 107274 |
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Main Authors | , , , , |
Format | Journal Article |
Language | English |
Published |
Elsevier B.V
01.04.2021
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Online Access | Get full text |
ISSN | 0167-8809 1873-2305 |
DOI | 10.1016/j.agee.2020.107274 |
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Abstract | •Cover crops reduced nitrate in the upper 60–120 cm soil depths in the fall.•Winter cereal monoculture covers resulted in low spring topsoil and subsoil nitrate.•Covers with radish or legume resulted in low subsoil but high topsoil nitrate.•Winter cereal monoculture covers immobilized N and restrained spring corn growth.•Fertilized corn yielded more after radish or no cover than after monoculture cereal.
In the mid-Atlantic USA region, nitrogen uptake by crops ceases about four weeks prior to harvest maturity, leaving substantial mineral N in the soil profile, which is prone to leach during the winter. Deep-rooted cover crops planted by early-September can potentially take up residual N and recycle some of it for following cash crops. We performed experiments on 19 minimum-tillage, grain farms investigating four unfertilized cover crop systems (forage radish (Raphanus sativus L.), winter cereal or grass, forage radish + winter cereal + crimson clover (Trifolium incarnatum L.), and a no cover crop control). We measured cover crop biomass, N uptake, and inorganic N distribution within the upper 210 cm of soil in late-fall and early-spring, and the following corn (Zea mays L.) crop’s growth and yield. In late-fall, radish reduced soil NO3 in the upper 90 cm by 66 %, while winter cereal or mix cover crops reduced NO3 in the upper 60 cm by 67 % and 56 %, respectively, compared to a no cover crop control. In the spring, the radish and mix cover crops resulted in comparable nitrate levels to the no cover crop control in the topsoil layer (> 30 kg ha−1) and less nitrate than the no cover crop control in subsoil layers. The winter cereal cover crop had low nitrate levels in the topsoil (∼20 kg ha−1) layer and subsoil layers. The biomass and N content of corn seedling (5 leaf) were influenced by the previous cover crop treatment in the order radish (4.0 g biomass plant−1) > mix (3.0 g biomass plant−1) = control (3.5 g biomass plant−1) > winter cereal (2.4 g biomass plant−1). At the farmers’ standard N fertilizer application rate, corn yield following radish was higher than following the winter cereal or mixed species cover crop but corn yield following radish was not different than following no cover crop. Corn yield following the winter cereal cover crop was lower than following no cover crop. Cover crops can be fit within the framework of existing cropping systems to scavenge residual N, therein reducing subsoil inorganic N. Radish and mixed species cover crops can be used prior to corn without reducing the overall short-term N use efficiency of the cropping system. |
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AbstractList | In the mid-Atlantic USA region, nitrogen uptake by crops ceases about four weeks prior to harvest maturity, leaving substantial mineral N in the soil profile, which is prone to leach during the winter. Deep-rooted cover crops planted by early-September can potentially take up residual N and recycle some of it for following cash crops. We performed experiments on 19 minimum-tillage, grain farms investigating four unfertilized cover crop systems (forage radish (Raphanus sativus L.), winter cereal or grass, forage radish + winter cereal + crimson clover (Trifolium incarnatum L.), and a no cover crop control). We measured cover crop biomass, N uptake, and inorganic N distribution within the upper 210 cm of soil in late-fall and early-spring, and the following corn (Zea mays L.) crop’s growth and yield. In late-fall, radish reduced soil NO₃ in the upper 90 cm by 66 %, while winter cereal or mix cover crops reduced NO₃ in the upper 60 cm by 67 % and 56 %, respectively, compared to a no cover crop control. In the spring, the radish and mix cover crops resulted in comparable nitrate levels to the no cover crop control in the topsoil layer (> 30 kg ha⁻¹) and less nitrate than the no cover crop control in subsoil layers. The winter cereal cover crop had low nitrate levels in the topsoil (∼20 kg ha⁻¹) layer and subsoil layers. The biomass and N content of corn seedling (5 leaf) were influenced by the previous cover crop treatment in the order radish (4.0 g biomass plant⁻¹) > mix (3.0 g biomass plant⁻¹) = control (3.5 g biomass plant⁻¹) > winter cereal (2.4 g biomass plant⁻¹). At the farmers’ standard N fertilizer application rate, corn yield following radish was higher than following the winter cereal or mixed species cover crop but corn yield following radish was not different than following no cover crop. Corn yield following the winter cereal cover crop was lower than following no cover crop. Cover crops can be fit within the framework of existing cropping systems to scavenge residual N, therein reducing subsoil inorganic N. Radish and mixed species cover crops can be used prior to corn without reducing the overall short-term N use efficiency of the cropping system. •Cover crops reduced nitrate in the upper 60–120 cm soil depths in the fall.•Winter cereal monoculture covers resulted in low spring topsoil and subsoil nitrate.•Covers with radish or legume resulted in low subsoil but high topsoil nitrate.•Winter cereal monoculture covers immobilized N and restrained spring corn growth.•Fertilized corn yielded more after radish or no cover than after monoculture cereal. In the mid-Atlantic USA region, nitrogen uptake by crops ceases about four weeks prior to harvest maturity, leaving substantial mineral N in the soil profile, which is prone to leach during the winter. Deep-rooted cover crops planted by early-September can potentially take up residual N and recycle some of it for following cash crops. We performed experiments on 19 minimum-tillage, grain farms investigating four unfertilized cover crop systems (forage radish (Raphanus sativus L.), winter cereal or grass, forage radish + winter cereal + crimson clover (Trifolium incarnatum L.), and a no cover crop control). We measured cover crop biomass, N uptake, and inorganic N distribution within the upper 210 cm of soil in late-fall and early-spring, and the following corn (Zea mays L.) crop’s growth and yield. In late-fall, radish reduced soil NO3 in the upper 90 cm by 66 %, while winter cereal or mix cover crops reduced NO3 in the upper 60 cm by 67 % and 56 %, respectively, compared to a no cover crop control. In the spring, the radish and mix cover crops resulted in comparable nitrate levels to the no cover crop control in the topsoil layer (> 30 kg ha−1) and less nitrate than the no cover crop control in subsoil layers. The winter cereal cover crop had low nitrate levels in the topsoil (∼20 kg ha−1) layer and subsoil layers. The biomass and N content of corn seedling (5 leaf) were influenced by the previous cover crop treatment in the order radish (4.0 g biomass plant−1) > mix (3.0 g biomass plant−1) = control (3.5 g biomass plant−1) > winter cereal (2.4 g biomass plant−1). At the farmers’ standard N fertilizer application rate, corn yield following radish was higher than following the winter cereal or mixed species cover crop but corn yield following radish was not different than following no cover crop. Corn yield following the winter cereal cover crop was lower than following no cover crop. Cover crops can be fit within the framework of existing cropping systems to scavenge residual N, therein reducing subsoil inorganic N. Radish and mixed species cover crops can be used prior to corn without reducing the overall short-term N use efficiency of the cropping system. |
ArticleNumber | 107274 |
Author | Weil, Ray R. Nichols, Kelly Hirsh, Sarah M. Duiker, Sjoerd W. Graybill, Jeff |
Author_xml | – sequence: 1 givenname: Sarah M. surname: Hirsh fullname: Hirsh, Sarah M. email: shirsh@umd.edu organization: Department of Environmental Science and Technology, University of Maryland, College Park, MD 20742, USA – sequence: 2 givenname: Sjoerd W. surname: Duiker fullname: Duiker, Sjoerd W. organization: Department of Plant Science, Penn State University, University Park, PA 16802, USA – sequence: 3 givenname: Jeff surname: Graybill fullname: Graybill, Jeff organization: Penn State Extension, Lancaster County, 1383 Arcadia Rd #140, Lancaster, PA, 17601, USA – sequence: 4 givenname: Kelly surname: Nichols fullname: Nichols, Kelly organization: Penn State Extension, Franklin County, 181 Franklin Farm Lane, Chambersburg, PA 17202, USA – sequence: 5 givenname: Ray R. surname: Weil fullname: Weil, Ray R. organization: Department of Environmental Science and Technology, University of Maryland, College Park, MD 20742, USA |
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Keywords | Subsoil Corn yield Nitrogen capture Fertilizer response Catch crop Residual nitrogen |
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Snippet | •Cover crops reduced nitrate in the upper 60–120 cm soil depths in the fall.•Winter cereal monoculture covers resulted in low spring topsoil and subsoil... In the mid-Atlantic USA region, nitrogen uptake by crops ceases about four weeks prior to harvest maturity, leaving substantial mineral N in the soil profile,... |
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SubjectTerms | agriculture autumn biomass cash crops Catch crop corn Corn yield cover crops cropping systems ecosystems environment farms fertilizer rates Fertilizer response forage grasses leaves minimum tillage nitrates nitrogen Nitrogen capture nitrogen content nitrogen fertilizers nutrient use efficiency radishes Raphanus sativus recycling Residual nitrogen seedlings soil profiles spring Subsoil topsoil Trifolium incarnatum winter Zea mays |
Title | Scavenging and recycling deep soil nitrogen using cover crops on mid-Atlantic, USA farms |
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