20 March 2012 Ankur R Desai Ecometeorology Lab CCR-SAGE Symposium Or… Why Climate Scientists will never hug Ecologists again Or why CCR and SAGE need each.
Download ReportTranscript 20 March 2012 Ankur R Desai Ecometeorology Lab CCR-SAGE Symposium Or… Why Climate Scientists will never hug Ecologists again Or why CCR and SAGE need each.
20 March 2012 Ankur R Desai Ecometeorology Lab CCR-SAGE Symposium Or… Why Climate Scientists will never hug Ecologists again Or why CCR and SAGE need each other more than ever… Arrhenius, S., 1896. On the influence of carbonic acid in the air upon the temperature of the ground. if the quantity of carbonic acid increases in geometric progression, the augmentation of the temperature will increase nearly in arithmetic progression Double CO2 -> 5-6 C increase Callendar, G.S., 1938. The artificial production of carbon dioxide and its influence on climate. QJRMS, 64, 233-240. If only were it so simple… The Beat Goes On… Data: NOAA/ESRL Image: They Might Be Giants Biology drives Physics Houghton et al. (2007) And we fail at modeling it… Feedbacks are ubiquitous and unconstrained Friedlingstein et al., 2006 Why? xkcd.com Light Schaefer et al., submitted Farquhar vs LUE Long et al., 2006 C3 vs C4 Temperature and Humidity Yi et al., 2011 n FOCUS | REVIEW ARTICLE NATURE GEOSCIENCE DOI: 10.1038/ NGEO844 Box 1 | Conceptual scheme depicting the mechanisms that explain the nitrogen-induced response of below-ground carbon cycling and its variation. Figure 1 | E ect of experimental nitrogen addition on various forest carbon pools and fluxes as calculated by meta-analysis. Positive values indicate that nitrogen addition had a positive e ect, negative values indicate a decrease. Error bars indicate the 95% confidence interval. Data are the weighted means for n data points (right axis). Parameters listed are carbon inputs (lef t axis): litter fall (LF) and fine-root production (FRP); carbon pools: t otal tree biomass (TB), microbial biomass (Cmic) and soil carbon content (Soil C); and carbon losses: litter decomposition (LD), heterotrophic respiration (Rh), root respiration (Rr) and soil carbon dioxide e ux (SCE). Exact numbers can be found in Supplementary Table S1. Reduced soil respiration Nitrogen deposition Neutral to positive e ect on photosynthesis Enhanced formation of recalcitrant compounds Reduced nitrogen limitation Reduced saprotrophic respiration Allocation shift (–) Recalcitrant Recalcitrant SOC SOC (+) Labile Liable SOC SOC Saprotrophic microbes Wood growth Microbial community shifts and/ or decomposing-enzyme shifts Reduced priming Rhizospheric microbes Reduced rhizospheric respiration Reduced SOC inputs Reduced carbon tr ansfer to rhizosphere Increased carbon limitation studies lasting longer than two years. Given that forest litter con- trenching technique31 — both of which physically sepa from root inputs. Our statistical meta-analysis revealed that the avera of heterotrophic respiration to nitrogen addition is pronounced than that of leaf-litter decomposition alon over 36 nitrogen-manipulation studies in forest heterotrophic respiration declined by 15% when n added (Fig. 1). Variation between experiments was responses ranging from a reduction of 57% to a stimula (Fig. 2). Forests exposed to elevated atmospheric nitr sition are also observed to have lower heterotrophic than forests receiving background levels of nitrogen (wet deposition <5.5 kg N ha–1 yr –1; Fig. 3a). For fore annual biomass production of around 600 g C m–2 yr –1 tion amounts to roughly 100 g C m–2 yr –1 (Fig. 3a). slopes of the two regressions in Fig. 3a further sugges gen deposition has a stronger negative e ect at highly sites, where nitrogen is unlikely to be the most limiti than at less productive sites, where nitrogen immo likely to be higher, and the negative e ect on heterotr ration is only marginal. It can be concluded that both addition of high amounts of fertilizer, and the chronic of small amounts of nitrogen, induce a decline in he soil respiration in most, but not all, forest ecosystems. [N] Reductionsin soil carbon dioxide e ux. Soil carbon d (SCE) is an important indicator of below-ground carbo Although heterotrophic respiration constitutes a substa SCE, two important carbon uxes, related to the prese in soils, di erentiate SCE from heterotrophic respirat major component of SCE is autotrophic in nature (root, and rhizosphere respiration), coupling variat Janssens ettemporal al., 2010 to variations in below-ground carbon allocation and Indirect Climate 1: Phenology Richardson et al., 2012 Indirect Climate 2: Water Sulman et al., 2012 Forest Succession Image: P. Curtis, Figure: Amiro et al., 2010 Pests Amiro et al., 2010 600 NEP (g C m-2 y-1) 400 200 0 Mountain Pine Beetle Forest Tent Caterpillar Gypsy Moth -200 -2 -1 0 1 2 3 Time since disturbance (years) 4 5 People! Gower et al., submitted What else? • • • • • • • • • Microbes, fungi, earthworms Herbivores (deer) Shading, resource competition Genetic variation Dispersal, recruitment, adaptation/evolution Fire, extreme events, feedbacks Acclimation Riverine export Ahhhh! It Matters… Friedlingstein et al., 2006 What to do? 4th Paradigm: Confronting science with intensive data NSF Advances in Biological Informatics M. Dietze, A. Desai, D. LeBauer, R. Kooper www.pecanproject.org