Abstract

Managed grassland is occasionally renovated to maintain plant productivity by killing old vegetation, ploughing, and reseeding. This study aimed to investigate the combined effect of grassland renovation and long-term manure application on the temporal dynamics of nitrous oxide (N2O) emission and nitrate nitrogen (NO3−–N) leaching. The study was conducted from September 2013 to September 2016 in a managed grassland renovated in September 2013. In this grassland, two treatments were managed—chemical fertilizer application (F treatment) and the combined application of chemical fertilizer and beef cattle manure (MF treatment)—for eight years before the renovation. The control treatment without fertilization (CT) was newly established in the F treatment. The soil N2O flux was measured using a closed chamber method. A leachate sample was collected using a tension-free lysimeter that was installed at the bottom of the Ap horizon (25 cm deep), and total NO3−–N leaching was calculated from leachate NO3−–N concentration and drainage volume was estimated by the water balance method. In the first year after renovation, the absence of plant nitrogen uptake triggered NO3−–N leaching following rainfall during renovation and increased drainage water after thawing. NO3−–N movement from topsoil to deeper soil enhanced N2O production and emission from the soil. N2O emission in MF treatment was 1.6–2.0 times larger than those of CT and F treatments, and NO3−–N leaching in MF treatment was 2.3–2.6 times larger than those of CT and F treatments in the first year. Mineral nitrogen release derived from long-term manure application increased NO3−–N leaching and N2O emission. In the second year, N2O emission and NO3−–N leaching significantly decreased from the first year because of increased plant N uptake and decreased mineral nitrogen surplus, and no significant differences in N2O emission and NO3−–N leaching were observed among the treatments. In the second and third years, NO3−–N leaching was regulated by plant nitrogen uptake. There were no significant differences in NO3−–N leaching among the treatments, but N2O emission in MF treatment was significantly smaller than in the F treatment. Long-term manure application could be a possible option to mitigate N2O emission in permanent grassland; however, the risk of increased NO3−–N leaching and N2O emission in the renovation year induced by manure nitrogen release should be noted.

Highlights

  • Permanent managed grassland is an important ecosystem for feeding in daily and beef farming systems

  • N content in surface soil and increased NO3 − –N leaching to 1 m depth, the same level as chemical fertilizer—the only application (400 kg N ha−1 ) in Andosol arable cropland in Japan. These results indicate that the mineral N supply from manure was a significant source of nitrous oxide (N2 O) emission and NO3 − –N leaching, especially in the field with repeated manure application

  • In the growing season in the third year, a large N2 O flux peak in F treatment was observed on 21 July 2016, while a leachate NO3 – –N concentration peak in F was observed on 3 August 2016. These dates were nine and 22 days after chemical fertilization (12 July 2016). These results indicate that the large N2 O flux in F in the third year was induced by N2 O production in topsoil before NO3 − –N leaching [28]

Read more

Summary

Introduction

Permanent managed grassland is an important ecosystem for feeding in daily and beef farming systems. The farmers continuously use managed grassland for several years and occasionally renovate grassland by ploughing and reseeding to maintain grassland productivity. Emission to the atmosphere and nitrate (NO3 − –N) leaching to the aquasphere [3]. Davies et al [2] showed that the net mineral N release after ploughing and reseeding was 85–140 kg N ha−1 higher than continued grassland in Scotland. Necpálová et al [3] showed ploughing and reseeding reduce the total N stock in surface soil by 14% and twofold, respectively, of N2 O emission and NO3 − –N leaching in Ireland pasture

Objectives
Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call