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Atmospheric Methane Distribution, Trend, and Linkage with Surface Ozone Arlene M. Fiore 1 Larry W. Horowitz 1, Ed Dlugokencky.

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Presentation on theme: "Atmospheric Methane Distribution, Trend, and Linkage with Surface Ozone Arlene M. Fiore 1 Larry W. Horowitz 1, Ed Dlugokencky."— Presentation transcript:

1 Atmospheric Methane Distribution, Trend, and Linkage with Surface Ozone Arlene M. Fiore 1 (arlene.fiore@noaa.gov), Larry W. Horowitz 1, Ed Dlugokencky 2, J. Jason West 3 1 NOAA Geophysical Fluid Dynamics Laboratory, Princeton, NJ 2 NOAA Global Monitoring Division, Earth System Research Laboratory, Boulder, CO 3 Atmospheric and Oceanic Sciences Program and Woodrow Wilson School, Princeton University, Princeton, NJ 1. Introduction REFERENCES Dentener, F., et al. (2003), J. Geophys. Res., 108, 4442, doi:10.1029/2002JD002916. Dlugokencky, E.J., et al. (2003), Geophys. Res. Lett., 30, 1992, doi:10.1029/2003GL018126. Dlugokencky, E.J., et al. (2005), J. Geophys. Res., 110, D18306, doi:10.1029/2005JD006035. Horowitz, L.W., et al. (2003), J. Geophys. Res., 108, 4784, doi:10.1029/2002JD002853. What is driving observed CH 4 trends? Does CH 4 source location influence the O 3 response? Methane (CH 4 ) emission controls can be a cost-effective strategy for abating both global surface ozone (O 3 ) and greenhouse warming [West and Fiore, 2005; see also poster by West et al.]  previous modeling studies used fixed CH 4 concentrations and globally uniform changes, but CH 4 is observed to vary spatially and temporally The major sink of CH 4 is reaction with tropospheric OH; emissions of CH 4 are shown in Section 2 Surface CH 4 rose by ~5-6 ppb yr -1 from 1990-1999, then leveled off (Section 3), possibly reflecting: (1) source changes of CH 4 [e.g. Langenfelds et al., 2002; Wang et al., 2004] or other species that influence OH [e.g. Karlsdóttir and Isaksen, 2000] (2) meteorologically-driven changes in the CH 4 sink [e.g. Warwick et al., 2002; Dentener et al., 2003; Wang et al., 2004] (3) an approach to steady-state with constant lifetime [Dlugokencky et al., 2003] Ozone response is largely independent of CH 4 source location 30% decrease in global anthropogenic CH 4 emissions reduces JJA U.S. surface afternoon O 3 by 1-4 ppbv BASE simulation (constant emissions) captures observed rate of CH 4 increase from 1990-1997, and leveling off post-1998 ANTH emissions improve modeled CH 4 post-1998 Wetland emissions in ANTH+BIO best match the observed CH 4 seasonality, interhemispheric gradient, and global mean trend  CH4 decreases by ~2% from 91-95 to 00-04 due to warmer temperatures (35%) and higher OH (65%, resulting from a ~10% increase in lightning NO x emissions) Future research should: consider climate-driven feedbacks from fire and biogenic emissions on  CH4 develop more physically-based parameterizations of lightning NO x emissions to determine whether higher emissions are a robust feature of a warmer climate Van Aardenne, J.A., F. Dentener, J.G.J. Olivier and J.A.H.W. Peters (2005), The EDGAR 3.2 Fast Track 2000 dataset (32FT2000). Wang, J.S., et al. (2004), Global Biogeochem. Cycles, 18, GB3011, doi:10.1029/2003GB002180. Warwick, N.J., et al. (2002), Geophys. Res. Lett., 29 (20), 1947, doi:10.1029/2002GL015282 West, J.J. and A.M. Fiore (2005), Environ. Sci. & Technol., 39, 4685-4691. Karlsdóttir, S., and I.S.A. Isaksen (2000), Geophys. Res. Lett., 27 (1), 93-96. Langenfelds, R.L., et al. (2002), Global Biogeochem. Cycles, 16, 1048, doi:10.1029/2001GB001466. Olivier, J.G.J., et al. (1999), Environmental Science & Policy, 2, 241-264. Olivier, J.G.J. (2002) In: "CO2 emissions from fuel combustion 1971-2000", 2002 Edition, pp. III.1-III.31. International Energy Agency (IEA), Paris. ISBN 92-64-09794-5. 3. Influence of Sources on Surface CH 4 Distribution and Trend OBSERVED BASE too low post-1998 ANTH improves CH 4 vs. OBS post-1998 ANTH+BIO best captures measured abundances Global mean surface CH 4 concentrations as measured (or sampled in the model) at 42 Global Monitoring Division (GMD) stations [e.g. Dlugokencky et al., 2005] with an 8-year minimum record. Values are area-weighted after averaging in latitudinal bands (60-90N, 30- 60N, 0-30N, 0-30S, 30-90S). Mean model bias and correlation with 1990-2004 monthly mean surface GMD observations BASE ANTH ANTH+BIO -90 -50 0 50 90 Latitude 100 50 0 -50 -100 Bias (ppb) r2r2 1.0 0.8 0.6 0.4 0.2 0.0 -0.2 BASE wetland emissions yield a closer match with observed CH 4 in tropics nmol/mol = ppb in dry air 2. Methane in the MOZART-2 CTM BASE Constant emissions (1990) Sensitivity simulations applying different CH 4 emission inventories: ANTH Time-varying anthropogenic emissions ANTH + BIO Time-varying anthropogenic and wetland emissions EDGAR v3.2 1990,1995 and “FAST-TRACK” 2000 anthrop. emissions [Olivier, 2002; van Aardenne et al., 2005] Biogenic source adjusted to match BASE 1990 total Tg CH 4 yr -1 Apply climatological mean post-1998, scaled to equal biogenic total in ANTH (224 Tg yr -1 ) From Wang et al. [2004 ] 6. Conclusions OBS (GMD) BASE ANTH ANTH+BIO ANTH+BIO improves: (1) High N latitude seasonal cycle, (2) Trend, (3) Low bias at S Pole, especially post-1998 1900 1850 1800 1840 1820 1800 1780 1760 1740 1800 1750 1700 1740 1720 1700 1680 1660 1640 1990 1995 2000 2005 Alert (82.4N,62.5W) South Pole (89.9S,24.8W) Mahe Island (4.7S,55.2E) Midway (28.2N,177.4W) Surface CH 4 concentrations at selected GMD stations nmol/mol = ppb in dry air Tropospheric O 3 response to anthropogenic CH 4 emission changes is approximately linear 5. Ozone Response to CH 4 Emission Controls  Stronger sensitivity in NO x -saturated regions (Los Angeles), partially due to local O 3 production from CH 4  O 3 change independent of CH 4 source location except for <10% effects in the Asian source region Latitudinal distribution of 1990 CH 4 emissions for cases shown below BASE ANTH ANTH+BIO -90 -50 0 50 90 Latitude 80 60 40 20 0 Tg CH 4 yr -1 4. Meteorologically-driven Changes in the CH 4 Lifetime  Meteorological drivers for trend  Not just an approach to steady-state Global mean surface CH 4 in BASE simulation (constant emissions)  Recycled NCEP 1990-2004 CH 4 Lifetime Against Tropospheric OH  Mean annual CH 4 lifetime shortens 10.40 10.23 Deconstruct   from 91-95 to 00-04 into individual contributions by varying T and OH separately  OH increases in the model by +1.4% due to a 0.3 Tg N yr -1 increase in lightning NO x ANTH+BIO best captures the CH 4 interhemispheric gradient ANTH+BIO improves the correlation with with observations at high northern latitudes 547 Tg CH 4 yr -1 Biogenic and biomass burning from Horowitz et al. [2003] Anthropogenic (energy, rice, ruminants) from EDGAR 2.0 [Olivier et al., 1999] Change in mean (  ) from 90-95 to 00-04 (years) + = BASE  T(+0.3K)  OH(+1.4%) ~100 gas and aerosol species, ~200 reactions NCEP meteorology 1990-2004 1.9 o latitude x 1.9 o longitude x 64 vertical levels detailed description in Horowitz et al. [2003] Change in summertime U.S. afternoon surface O 3 MEAN DIFFERENCEMAX DAILY DIFFERENCE ZERO ASIAN ANTHROP. CH 4 GLOBAL 30% DECREASE IN ANTHROP. CH 4 ppbv Simulations of anthropogenic CH 4 emission reductions (relative to BASE)  tropospheric O 3 (Tg) Year  surface CH 4 (ppb) Change in CH 4 and O 3 approaching steady-state after 30 years BASE captures observed rate of increase 1990-97 and leveling off after 1998 547548557 Tg CH 4 yr -1 199019952000 MOZART-2 (this work) TM3 [Dentener et al., ACPD, 2005] GISS [Shindell et al., GRL, 2005 GEOS-CHEM [Fiore et al., GRL, 2002] IPCC TAR [Prather et al., 2001] X 0 4 9 13 17 21 29


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