A Look at Amazon Basin Seasonal Dynamics with the Biophysical ...
A Look at Amazon Basin Seasonal Dynamics with the Biophysical ... A Look at Amazon Basin Seasonal Dynamics with the Biophysical ...
Isotopic Signature of Nitrous Oxide in dry season forest soils -implications for seasonal production of N2OTibisay PerezSusan Trumbore, Plinio Barbosa de Camargo, Enir Salazar da Costa, StanlyTyler, Michael Keller, Patrick Crill and Eric DavidsonUniversity of CaliforniaMeasurements of stable isotopes in N 2 O provide useful constraints for the globalN 2 O. Tropical rain forest soils are the largest natural source of N 2 O to the atmosphere.Variations in the flux and isotopic signature of N 2 O from tropical soils reflectmicrobiological processes that produce and consume N 2 O, and physical controls of therate at which N 2 O escapes from the soil pore space to the overlying atmosphere. Ourprevious work in the Amazon basin and in a Costa Rican forest suggested that soil textureaffects the isotopic composition of the N 2 O emitted from the soil surface. We presenthere measurements of N 2 O isotopic composition across a soil texture gradient during thedry season of 2001 in the N 2 O Tapajós National Forest (TNF), Para State, Brazil. Weselected three soil types within the TNF (km 83 site) for study: sandy, transitional (sand +clay) and clay soils. Soil pits (0 to 2 m) were dug at each site and sampled for soilcharacteristics, and tubes for sampling soil gases were installed in each pit. We alsocollected samples at a dry down experiment (TNF, km 67) at 4 pits (0-11 m depth) tocompare variability in the N 2 O isotopic composition affected by drought and at greaterdepths. During the dry season at all sites the N 2 O mixing ratio in soil air increased withdepth from ~340 ppb near the surface to ~600 ppb in the sandy soil (2 m depth) and to~2000 ppb in the transition and clay soils (2 m depth) of the km 83 site. At the km 67site the mixing ratio increased to 1000 ppb at 11 m. The isotopic signature of δ 15 N andδ 18 O of N 2 O and became more depleted in heavy isotopes with depth at all sites. Theδ 15 N 2 O values ranged from 3 to 4 ‰ in the surface to ~2 at 2 m depth in the sandy soiland to ~-4 ‰ in the transition and clay soils at 2m depth. We suggest that little is N 2 O isproduced in these soils during the dry season and that most of the N 2 O emitted during thistime was produced during the wet season and is being slowly released from the large soilcolumn to the atmosphere. Modeling of the diffusion of gases from the soil columnsupports this hypothesis, as do the N 2 O isotopic differences observed between soils withdifferent texture. Soils with higher overall effective diffusivity (sandy soil) release theN 2 O faster than the more compacted soils (e.g. clay and transitional) and therefore havelower N 2 O concentrations at depth and N 2 O with an isotopic value closer to that of theatmospheric N 2 O compared to the soils that have less effective diffusivity.
- Page 272: Response of photosynthesis to diffe
- Page 276: 1 Trumbore et al., 1996
- Page 280: Effect of Soil Texture on Carbon Dy
- Page 284: Relationship Between Litter Product
- Page 288: Regrowth Biomass Estimation in the
- Page 292: Effects of Interannual Climate Vari
- Page 296: Carbon balance and vegetation dynam
- Page 300: SOIL CARBON STOCKS INFLUENCED BY LI
- Page 304: Drought effects on net primary prod
- Page 308: COARSE WOOD DEBRIS DEPOSITION, DECO
- Page 312: Soil properties and carbon sequestr
- Page 316: Patiño, S. 1,2,a , Mercado, L. 2 ,
- Page 320: Where are the oldest of the forest?
- Page 326: Ecosystem degradation due to fire &
- Page 330: AbstractMulti-temporal Analysis of
- Page 334: ABSTRACT - Second International LBA
- Page 338: Mapping Biomass Loss from Forest Fi
- Page 342: Spatial and Temporal Drivers of Fir
- Page 346: A new method to detect forest fire
- Page 350: Forest Canopy Damage from Selective
- Page 354: AcknowledgementsSupport of this res
- Page 358: Carbon Storage in Soils from Degrad
- Page 362: An improved soil water budget model
- Page 366: PATTERNS OF TREE MORTALITY IN FORES
- Page 370: RAIN WATER INTERCEPTION BY SELECTIV
Isotopic Sign<strong>at</strong>ure of Nitrous Oxide in dry season forest soils -implic<strong>at</strong>ions for seasonal production of N2OTibisay PerezSusan Trumbore, Plinio Barbosa de Camargo, Enir Salazar da Costa, StanlyTyler, Michael Keller, P<strong>at</strong>rick Crill and Eric DavidsonUniversity of CaliforniaMeasurements of stable isotopes in N 2 O provide useful constraints for <strong>the</strong> globalN 2 O. Tropical rain forest soils are <strong>the</strong> largest n<strong>at</strong>ural source of N 2 O to <strong>the</strong> <strong>at</strong>mosphere.Vari<strong>at</strong>ions in <strong>the</strong> flux and isotopic sign<strong>at</strong>ure of N 2 O from tropical soils reflectmicrobiological processes th<strong>at</strong> produce and consume N 2 O, and physical controls of <strong>the</strong>r<strong>at</strong>e <strong>at</strong> which N 2 O escapes from <strong>the</strong> soil pore space to <strong>the</strong> overlying <strong>at</strong>mosphere. Ourprevious work in <strong>the</strong> <strong>Amazon</strong> basin and in a Costa Rican forest suggested th<strong>at</strong> soil textureaffects <strong>the</strong> isotopic composition of <strong>the</strong> N 2 O emitted from <strong>the</strong> soil surface. We presen<strong>the</strong>re measurements of N 2 O isotopic composition across a soil texture gradient during <strong>the</strong>dry season of 2001 in <strong>the</strong> N 2 O Tapajós N<strong>at</strong>ional Forest (TNF), Para St<strong>at</strong>e, Brazil. Weselected three soil types <strong>with</strong>in <strong>the</strong> TNF (km 83 site) for study: sandy, transitional (sand +clay) and clay soils. Soil pits (0 to 2 m) were dug <strong>at</strong> each site and sampled for soilcharacteristics, and tubes for sampling soil gases were installed in each pit. We alsocollected samples <strong>at</strong> a dry down experiment (TNF, km 67) <strong>at</strong> 4 pits (0-11 m depth) tocompare variability in <strong>the</strong> N 2 O isotopic composition affected by drought and <strong>at</strong> gre<strong>at</strong>erdepths. During <strong>the</strong> dry season <strong>at</strong> all sites <strong>the</strong> N 2 O mixing r<strong>at</strong>io in soil air increased <strong>with</strong>depth from ~340 ppb near <strong>the</strong> surface to ~600 ppb in <strong>the</strong> sandy soil (2 m depth) and to~2000 ppb in <strong>the</strong> transition and clay soils (2 m depth) of <strong>the</strong> km 83 site. At <strong>the</strong> km 67site <strong>the</strong> mixing r<strong>at</strong>io increased to 1000 ppb <strong>at</strong> 11 m. The isotopic sign<strong>at</strong>ure of δ 15 N andδ 18 O of N 2 O and became more depleted in heavy isotopes <strong>with</strong> depth <strong>at</strong> all sites. Theδ 15 N 2 O values ranged from 3 to 4 ‰ in <strong>the</strong> surface to ~2 <strong>at</strong> 2 m depth in <strong>the</strong> sandy soiland to ~-4 ‰ in <strong>the</strong> transition and clay soils <strong>at</strong> 2m depth. We suggest th<strong>at</strong> little is N 2 O isproduced in <strong>the</strong>se soils during <strong>the</strong> dry season and th<strong>at</strong> most of <strong>the</strong> N 2 O emitted during thistime was produced during <strong>the</strong> wet season and is being slowly released from <strong>the</strong> large soilcolumn to <strong>the</strong> <strong>at</strong>mosphere. Modeling of <strong>the</strong> diffusion of gases from <strong>the</strong> soil columnsupports this hypo<strong>the</strong>sis, as do <strong>the</strong> N 2 O isotopic differences observed between soils <strong>with</strong>different texture. Soils <strong>with</strong> higher overall effective diffusivity (sandy soil) release <strong>the</strong>N 2 O faster than <strong>the</strong> more compacted soils (e.g. clay and transitional) and <strong>the</strong>refore havelower N 2 O concentr<strong>at</strong>ions <strong>at</strong> depth and N 2 O <strong>with</strong> an isotopic value closer to th<strong>at</strong> of <strong>the</strong><strong>at</strong>mospheric N 2 O compared to <strong>the</strong> soils th<strong>at</strong> have less effective diffusivity.