N2O AND NO EMISSIONS FROM POULTRY LITTER AND UREA APPLICATIONS TO BERMUDA GRASS

Citation
Fc. Thornton et al., N2O AND NO EMISSIONS FROM POULTRY LITTER AND UREA APPLICATIONS TO BERMUDA GRASS, Atmospheric environment, 32(9), 1998, pp. 1623-1630
Citations number
39
Categorie Soggetti
Environmental Sciences","Metereology & Atmospheric Sciences
Journal title
ISSN journal
13522310
Volume
32
Issue
9
Year of publication
1998
Pages
1623 - 1630
Database
ISI
SICI code
1352-2310(1998)32:9<1623:NANEFP>2.0.ZU;2-F
Abstract
The objectives of the study were to quantify N2O and NO emissions from poultry litter and urea applications to Bermuda grass (Cynodaon dacty lon L.) and examine the seasonal variations in emissions. Soil N2O and NO emissions were measured in a Bermuda grass pasture treated with tw o sources of poultry litter, composted poultry litter (CPL) and fresh poultry litter (FPL) and urea (URE). Nitrogen (N) was applied to suppl y 336 kg available N ha(-1) in four split applications made during the period from April to August 1995. An automated closed chamber system was employed to monitor N2O and NO emissions. The seasonal N2O emissio n patterns were characterized by several peaks occurring in phase with intermittent rain events and increasing soil N and organic carbon (C) associated with fertilizer application. The cumulative N2O emissions over the season (May to mid September) from the various treatments wer e, 3.87 kg N ha(-1) from FPL, 2.96 kg N ha(-1) from URE, and 1.64 kg N ha(-1) from CPL. These seasonal N2O losses accounted for 1.0, 0.73 an d 0.32% of the added available N for the, FPL, URE and CPL treatments, respectively. Denitrification was suggested as the primary source of N2O following rain events when inorganic N and C soil concentrations w ere highest and soil water-filled-pore-space (WFPS) was elevated. Peak s in NO emissions were observed primarily immediately after the additi on of N sources. The seasonal NO emissions were smaller and ranged fro m 1.36 kg N ha(-1) for URE, and 0.97 kg N ha(-1) for FPL, to 0.47 kg N ha(-1) for CPL. The seasonal NO emissions accounted for 0.36, 0.24 an d 0.09% of the added N for the URE, FPL, and CPL treatments, respectiv ely. Published by Elsevier Science Ltd.