SSSAJ Journal of Natural Resources and Life Sciences Education
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


This Article
Right arrow Figures Only
Right arrow Full Text Free
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Web of Science (6)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Stevens, R. J.
Right arrow Articles by Laughlin, R. J.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Stevens, R. J.
Right arrow Articles by Laughlin, R. J.
Agricola
Right arrow Articles by Stevens, R. J.
Right arrow Articles by Laughlin, R. J.
Related Collections
Right arrow Nutrient Management
Right arrow Soil Biochemistry
Right arrow Animal Waste
Soil Science Society of America Journal 66:647-652 (2002)
© 2002 Soil Science Society of America


DIVISION S-8—NUTRIENT MANAGEMENT & SOIL & PLANT ANALYSIS

Cattle Slurry Applied Before Fertilizer Nitrate Lowers Nitrous Oxide and Dinitrogen Emissions

R. James Stevens* and Ronald J. Laughlin

Department of Agriculture and Rural Development, Agricultural and Environmental Science Division, Newforge Lane, Belfast BT9 5PX, UK

* Corresponding author (jim.stevens{at}dardni.gov.uk)

Nitrous oxide emissions increase because of denitrification in the first few days after cattle (Bos taurus) slurry (CS) is applied to grassland soils fertilized with NO3. Denitrifying conditions are created when the readily decomposable C in the CS is oxidized by the soil microbial biomass when NO3 is present and O2 is deficient. Half of the readily decomposable C in CS can be volatile fatty acids (VFAs) that take up to 4 d to degrade. The timing of CS application relative to fertilizer-NO3 application could therefore affect the losses of N2O and N2. We used the 15N gas-flux method to measure N2O and N2 fluxes from grassland when CS containing 60 kg NH4-N ha-1 was applied 4, 3, 2, 1, and 0 d before the application of 60 kg N ha-1 of K15NO3. For a field experiment repeated in April, May, August, and October 1998, CS applied 3 or 4 d before KNO3 had no significant effect in any month on the flux of N2O in the 124 h after KNO3 application. On average over all months, the extra emission of N2O-N over the control was equivalent to 0.8, 1.1, and 2.9% of KNO3-N for prior applications of CS at 2, 1, and 0 d, respectively. When CS was applied 4 d prior to KNO3 there was no significant effect on the flux of N2 in any month. The maximum loss of N2O + N2 was 8.3% of the KNO3 applied (5 kg N ha-1) when CS and KNO3 were applied at the same time in April.

Abbreviations: CS, cattle slurry • VFA, volatile fatty acid • WFPS, water-filled pore space







HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Vadose Zone Journal
Journal of Plant Registrations Journal of
Environmental Quality
The Plant Genome
Copyright © 2002 by the Soil Science Society of America.