Effect of cattle urine addition on the surface emissions and subsurface concentrations of greenhouse gases in a UK peat grassland

•We present surface fluxes and subsurface CO2, CH4 and N2O from a grazed UK peatland.•Cattle urine increased N2O fluxes due to high NO3− in surface soil layers.•Addition of cattle urine increased subsurface CH4 and N2O concentrations.•N2O production at depth continued long after emissions were detec...

Ausführliche Beschreibung

Gespeichert in:
Bibliographische Detailangaben
Veröffentlicht in:Agriculture, ecosystems & environment ecosystems & environment, 2014-03, Vol.186, p.23-32
Hauptverfasser: Boon, A., Robinson, J.S., Chadwick, D.R., Cardenas, L.M.
Format: Artikel
Sprache:eng
Schlagworte:
Online-Zugang:Volltext
Tags: Tag hinzufügen
Keine Tags, Fügen Sie den ersten Tag hinzu!
Beschreibung
Zusammenfassung:•We present surface fluxes and subsurface CO2, CH4 and N2O from a grazed UK peatland.•Cattle urine increased N2O fluxes due to high NO3− in surface soil layers.•Addition of cattle urine increased subsurface CH4 and N2O concentrations.•N2O production at depth continued long after emissions were detected at the surface.•Urine addition had little long-term impact on CO2 production or emission. Grazing systems represent a substantial percentage of the global anthropogenic flux of nitrous oxide (N2O) as a result of nitrogen addition to the soil. The pool of available carbon that is added to the soil from livestock excreta also provides substrate for the production of carbon dioxide (CO2) and methane (CH4) by soil microorganisms. A study into the production and emission of CO2, CH4 and N2O from cattle urine amended pasture was carried out on the Somerset Levels and Moors, UK over a three-month period. Urine-amended plots (50gNm−2) were compared to control plots to which only water (12mgNm−2) was applied. CO2 emission peaked at 5200mgCO2m−2d−1 directly after application. CH4 flux decreased to −2000μgCH4m−2d−1 two days after application; however, net CH4 flux was positive from urine treated plots and negative from control plots. N2O emission peaked at 88mgN2Om−2d−1 12 days after application. Subsurface CH4 and N2O concentrations were higher in the urine treated plots than the controls. There was no effect of treatment on subsurface CO2 concentrations. Subsurface N2O peaked at 500ppm 12 days after and 1200ppm 56 days after application. Subsurface NO3− concentration peaked at approximately 300mgNkg dry soil−1 12 days after application. Results indicate that denitrification is the key driver for N2O release in peatlands and that this production is strongly related to rainfall events and water-table movement. N2O production at depth continued long after emissions were detected at the surface. Further understanding of the interaction between subsurface gas concentrations, surface emissions and soil hydrological conditions is required to successfully predict greenhouse gas production and emission.
ISSN:0167-8809
1873-2305
DOI:10.1016/j.agee.2014.01.008