Figures Summarizing the Global Cycles of Biogeochemically Important Elements Author(s): William S. Reeburgh Reviewed work(s): Source: Bulletin of the Ecological Society of America, Vol. 78, No. 4 (Oct., 1997), pp. 260-267 Published by: Ecological Society of America Stable URL: http://www.jstor.org/stable/20168182 . Accessed: 16/02/2012 05:36 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. Ecological Society of America is collaborating with JSTOR to digitize, preserve and extend access to Bulletin of the Ecological Society of America. http://www.jstor.org Berkowitz, A. 1997. A simple frame the benefits work for considering partnerships. of student-scientist In TERC and Concord Consor report. tium (1997). Conference National Conference on Student & Scientist Partnerships. Education Resource Technical of in be teachers and scien Annual Meeting, Chi USA. R. F., and J. Northfield. The second article is by William S. Reeburgh, Earth System Science, Dr. University of California-Irvine. summaries Reeburgh has developed and graphical illustrations of global impor cycling of several extremely tant chemicals. These summaries and figures will be especially anyone teaching graduate ecology pertinent undergraduate courses. to and cycles of biologically are an important part of basic and advanced Earth Science, active elements and Ecology, courses. An Biogeochemistry understanding of bio and anthropo cycles genic impacts on them is also funda in studies of global climate mental geochemical 260 Bulletin of sci teachers. National Academy Press, Washington, D.C., USA. to live Norris, S. P. 1995. Learning with scientific expertise: toward a theory of intellectual communal ism for guiding science the Ecological Associates, Hillsdale, Jersey, USA. and Shulman, L. 1987. Knowledge teaching: foundations of the new reform. Harvard Educational Re teaching. S.A., and A.T. Jones. 1992. Open work in science: a review of Simon, existing cational practice. Resource Massachusetts, on Student 'TechnicalEducation Resource Center & 2067 Massachusetts Partnerships: Conference Technical Education Re Report. source Center, Cambridge, Massa chusetts, USA. and Ruopp, R., S. Gal, B. Drayton, M. Pfister. 1993. Labnet: community of practice. toward a Lawrance change. Unfortunately, most presen tations of biogeochemical cycles oc cupy one of two extremes: they are either presented so simply that they contain information on pathways only, or in such detail that they defy and are useful only to comprehension specialists. Further, most in facets specialized workers of indi and broad perspectives and an understanding of interactions cycles is lacking. between The figures presented here are an Cambridge, USA. Brian Drayton ",2 and Joni Falk' Scientist have Center, (1997). Na Consortium for Edu Conference on Student & Scientist Partnerships. Technical Education C. 1997. Why do scien tists want teachers and students to do real research? In TERC and Concord Center Studies, King's College, University of London, London, UK. TERC and Concord Consortium. 1997. Conference report. National ScienceEducation79(2):201-217. vidual cycles, FIGURES SUMMARIZING THE GLOBAL CYCLES OF BIOGEOCHEMICALLY IMPORTANTELEMENTS The global of ence tional Conference Illinois cago, (March 1997). D.C., USA. AERA, Washington, Fullan, M. 1991. The new meaning of educational change. Teachers Col lege Press, New York, New York, Gunstone, development Erlbaum New view 57(1):1-22. Jersey, USA. Pennypacker, tists in an innovative mentorship to collaboration. Paper presented Educational Research American Association New professional USA. education the relationships tween science lex, Norwood, (National Research Council). 1996. The role of scientists in the in the United States. Pages 45-59 M. Hale, editor. Ecology in educa tion. Cambridge University Press, Cambridge, UK. 1997. Dy Falk, J., and B. Drayton. namics ScienceEducation16(5):523-537. Lemke, J. 1993. Talking science: lan guage, learning, and values. Ab NRC Center, Cam bridge, Massachusetts, . 1993. Ecology 1994. Metacognition and learning to teach. International Journal of Avenue Cambridge, MA 02140 'Department of Biology Boston University Boston, MA 02215 E-mail: [email protected] [email protected] and use of color to distinguish pools, fluxes, and turnover times makes comprehension of individual element cycles and comparison between ele ment cycles straightforward. The figures were developed as in a graduate-level class assignments course in Earth Systems at the Uni Irvine and have versity of California, been used in graduate as well as un sur dergraduate courses. Discussion rounding these figures from "What do we do we has evolved include and which to fill the middle ground and between element comparisons cycles. Figures based on current lit the global erature values showing numbers allow being prepared, to a current "Where did these numbers come from?" To with the permit easy comparison of C, 0, N, S, P, and Si, as as well H20 and CH4, are presented in a uniform format that shows pool or original literature, we have used the fac unlits as published. Conversion tors are supplied in the captions. The cycles reservoir sizes, significant natural and transfers or fluxes be anthropogenic tween pools, and residence times esti mated from the ratio of pool size and the major fluxes. The uniform format Society of America arrows associated note the direction Black use?" as they were attempt with the fluxes de of the flux. and white as well as color versions of these figures will soon be at the Uni available for downloading Table 1. Reservoir sizes and turnover times of biologically Turnover time (yr) Quantity Element active elements. Irvine Depart versity of California, ment of Earth System Science Web I .ps.uci.edu_ site: <http://:ess reeburgh/figures.html>. Questions, corrections, updates, and suggestions should be addressed by e-mail to the Carbon (10's g C) Sediments, rocks Deep ocean (DIC) Soils Surface ocean Atmosphere Deep ocean (DOC) Terrestrial biomass Surface sediments Marine biomass >> 1 06 2000 <10-105 decades 5 5000 50 0.1-1000 0.1-1 77 x 106 38000 1500 1000 750 700 550-680 150 2 Oxygen (10'I mol 02) Sedimentary rocks Atmosphere Long-lived biota author. Acknowledgments These figures summarize the ef forts of several groups. The carbon cycle figure resulted from discussions at a 1993 Dahlem by participants on "The Role of Non Conference Living Organic Matter in the Global Cycle" (Zepp and Sonntag 1995). The carbon figure was used as the level a template and established Carbon 37000 180 106 3 x 106 1000 219 500 11 6 50 22 days Ocean Biota Surface ocean Nitrogen (1012 g N) Atmosphere (N2) Sediments Ocean (dissolved N2) Ocean (inorganic) Soil Terrestrial biomass Atmosphere (N20) Marine biomass Sulfur (1012 g S) Lithosphere Ocean Sediments Soils Lakes Marine biota Atmosphere 4x 5x 2.2 x 6x 3x 1.3 x 1.4 x 4.7 x 109 108 107 105 105 104 104 102 2x 3x 3x 3x 1010 109 101 105 300 30 4.8 107 107 1000 2000 50 102 of detail used for the other figures. Review articles and tables from text books provided the information used in the methane and water figures. The other figures were produced and re fined from 1993 through 1997 by graduate students in a core course of fered by the newly formed Depart ment of Earth System Science at the Irvine. Data of California, University for as the figures was assembled the figures were drafted discus after a thorough classroom homework; 108 106 106 103 3 1 8-25 days sion. The graduate students who con tributed to this effort are: Huisheng Bian, Paul Burke, Julia Gaudinski, Bryan Hannegan, Adam Hirsch, Jen nifer King, Caroline Masiello, Karena Seth Olsen, Tibisay Joe Selzler, Perez, Shannon Regli, and Chris Walker. David Valentine, W. H. Schlesinger and M. 0. Andreae also provided helpful comments. McKinney, Phosphorus (1012 g P) Sediments Land Deep ocean Terrestrial biota Surface ocean Atmosphere 4 x 109 2 x 105 8.7 x 104 3000 2700 2 x 108 2000 1500 -50 2.6 0.028 days Literature cited Water Water Vol. Oceans Polar ice, glacier Groundwater (actively exchanged) Freshwater lakes Saline lakes Soil moisture Rivers Atmospheric water vapor (103 km3) 1,370,000 29,000 4000 125 104 67 1.32 14 Percentage 97.61 2.08 0.29 0.009 0.008 0.005 0.005 0.0009 Turnover time (yr) 37,000 16,000 300 10-100 10-10,000 280 days 12-20 days 9 days J. W. 1992. The oceans. Murray, in S. S. Butcher, Pages 176-211 R. J. Charlson, G. H. Orians, and editors. Global G. V. Wolfe, bio geochemical cycles. Academic Press, San California, Diego, USA. Schlesinger, chemistry: W. H. 1991. an analysis Biogeo of global change. Academic Press, San Di ego, California, USA. October 1997 261 Carbon 411-454 Eswaran, H., E. Van den Berg, and P. 1993. Organic Reich. carbon in soils of the world. Soil Science Trace atmospheric constituents. of Society America J. I. geochemical cycles: Global bio progress and Chemistry Schimel, D. S., B. H. Braswell, E. A. Holland, R. McKeown, D. S. Ojima, T. H. Painter, W. J. Parton, and A. R. Townshend. edaphic 1994. Cli and biotic controls over storage and turnover of car bon in soils. Global Biogeochemi cal Cycles 8:279-293. Siegenthaler, U., and J. L. Sarmiento. 1993. Atmospheric carbon diox ide and the ocean. Nature 365:119-125. Nitrogen Burns, R. C., and R. W. 1975. Nitrogen F. Hardy. in bacteria fixation and higher plants. Springer Verlag, New John Wiley and Sons, New York, New York, USA. Oxygen 1992 problems. Marine 39:67-93. matic, editor. Journal 57:192-194. Hedges, in S. E. Schwartz, York, New York, USA. Keeling, R. F., R. P. Najjar, M. L. Bender, and P. P. Tans. 1993. What atmospheric oxygen mea surements can tell us about the global carbon geochemical cycle. Global Cycles 7:37-67. and J.-L. Rao. in sediments 1994. of the 2339. Jahnke, R. A. 1992. The phosphorus cycle. Pages 301-315 in S. S. Butcher, R. J. Charlson, G. H. Orians, and G. V. Wolfe, editors. biogeochemical cycles. Academic Press, San Diego, Cali fornia, USA. Meybeck, M. 1982. Carbon, nitrogen J. N., W. H. Schlesinger, Galloway, H. Levy II, A. Michaels, and J. L. Schnoor. 1995. Nitrogen fixation: phosphorus transport by world rivers. American Journal of Science 292:421-454. enhancement-en anthropogenic vironmental response. Global Bio geochemical Cycles 9:235-252. Jaffe, D. A. 1992. The nitrogen cycle. Pages 263-284 in S. S. Butcher, R. J. Charlson, G. H. Orians, and G. V. Wolfe, editors. Global bio Oxygen-phosphorus feedback and Colman, A. S., F. T. Mackenzie, H. D. Holland. 1997. Redox stabi lization of the atmosphere and oceans and marine productivity. Science 275:406-407. geochemical Press, San Academic cycles. Diego, California, USA. M. B., J. W. Elkins, S. C. and Y. L. Yung. 1976. Wofsy, Sources and sinks for atmospheric McElroy, N20. Review Space Physics W. Schlesinger, Hartley. of Geochemical and 14:143-150. and A. E. 1992. A global budget for H., atmospheric NH3. Biogeochemis try 15:191-211. Soderlund, R., and B. H. Svensson. 1976. The global nitrogen cycle. Ecological Bulletins-NFR 22:23 73. Stedman, D. H., and R. B. Schetter. 1983. The global budget of atmo spheric nitrogen species. Pages 262 Bulletin of the Ecological and Van Cappellen, P., and E. D. Ingall. 1996. Redox stabilization of the and oceans by phos atmosphere marine productiv phorus-limited ity. Science 271:493-496. Van Cappellen, P., and E. D. Ingall. P. Van 1997. Response by and E. D. Ingall. Sci Cappelen ence 275:407-408. Sulfur Andreae, 0. 1990. Ocean-atmo sphere interactions in the global biogeochemical sulfur cycle. Ma rineChemistry 30:1-29. Bates, T. S., B. K. Lamb, A. Guenther, J. Dignon, and R. B. Stoiber. 1992. Sulfur emission to the atmosphere from natural Society Butcher, R. J. Charlson, G. H. Orians, and G. V. Wolfe, editors. Global biogeochemical cycles. Academic Press, San Diego, Cali fornia, USA. D. M., of America P. Treguer, M. A. Brzezinski, A. Queguiner. 1995. Production and of biogenic silica in dissolution the ocean: Leynaert, and B. revised global esti mates, comparison with regional data and relationship to biogenic sedimentation. Global Bio geochemical Cycles 9:359-372. Treguer, P., D. M. Nelson, A. J. Van Benekom, Leynaert, The D. J. Demaster, A. and B. Queguiner. 1995. in the world silica balance ocean: a re-estimate. Science 268:375-379. Methane Cicerone, R. J., and R. S. Oremland. 1988. Biogeochemical aspects of atmospheric methane. Global Bio geochemical Cycles 2:299-327. Ehhalt, D. H. 1974. The atmospheric cycle of methane. Tellus 26:58 70. Fung, I., J. Lerner, L. Lerner, E. M. L. P. Matthews, Prather, and P. J. Fraser. 1991. Steele, model synthe Three-dimensional sis of the global methane cycle. Journal of Geophysical Research 96:13,033-13,065. Reeburgh, W. S., S. C. Whalen, and M. J. Alperin. 1993. The role of in the global meth methylotrophy ane budget. Pages 1-14 Murrell and D. P. Kelly, on Microbial growth pounds. M. of Atmospheric Charlson, R. J. , T. L. Anderson, and R. E. McDuff. 1992. The sulfur cycle. Pages 285-300 in S. S. Silica Nelson, Amazon River and estuary: impli cations for the global flux of phos phorus to the sea. Geochimica et Cosmochimica Acta 58:2333 Global Journal Bio Phosphorus Berner, R. A., Phosphorus sources. Chemistry 14:315-337. Intercept, in J. C. editors. com C, Andover, UK. Element cycles-reference volumes Berner, E. K., and R. A. Berner. 1996. Global environment,water, air and geochemical cycles. Prentice-Hall, Upper Saddle River, New Jersey,USA. Bolin, and R. B. Cook, B., 1983. The major editors. and their interactions. cycles on SCOPE (Scientific Committee 21. Problems of the Environment) Wiley, Chichester, UK. Butcher, S. S., R. J. Charlson, G. H. 1992. Orians, and G. V. Wolfe. cycles. biogeochemical Global Academic Press, San Diego, Cali fornia, USA. Ivanov, M. V., and J. R. Freney, tors. 1983. geochemical (Scientific lems of biogeochemical The global Committee on Prob the Environment) 19. Wiley, Chichester, UK. Likens, G. E. 1981. Some perspec tives on the major biogeochemical cycles. SCOPE (Scientific Com mittee on Problems of the Envi Chichester, ronment) 17. Wiley, Zepp, R. G., and Ch. Sonntag, edi tors. 1995. The role of nonliving organic matter in the earth's car bon cycle. Environmental Sci ences Research Report 16, Dahlem Workshop Reports. Wiley, New York, New York, USA. UK. W. Schlesinger, H. Bio 1997. William S. Reeburgh Earth System Science an analysis of glo geochemistry: bal change. Second edition. Aca demic Press, San Diego, Califor edi bio sulfur cycle. SCOPE University of California Irvine Irvine,CA 92697-3100 E-mail: nia, USA. reeburgh@ uci.edu Pools and fluxes inGt C and Gt C y', Gt = 10'5 g; *= living pools; (turnover times) Terrestrial Atmosphere Marine NPP =50( 1 Deforesta =41.4 y-'t Combustion (80's) 5.4 yr-t 750 (3 y) Ann. increment = 3.2 y-1 (- +1.5 ppmv C02 Y1) NPP = 50 y New production Rivers Plants* 550-680 peat 360 (50 y) o0.2 y-1 pDoOC:. POC: 0.2 y-1 Coastal Ocean 20% of NPP (> 1000 y) microbial* 15-30 (<10 y) POC 250-500 (<100 y) remainder 600-800 (102-1 05 y) Ocean CO Exchange 90anget80%9ofyNPP Open Ocean 80% of NPP POC 5, Living 2* m 100 = 10 y _____POC,l Surface Sediments 150 (0.1 -1000 y) (-1m) \ Deep 8 km 7 y POC 70-0 References: Sediments Hedges, 1992; Eswaran eta!., 1993; Siegenthaler & Sarmiento, 1993; Schimel et al., 1994 Respiration kerogen 15x106 (>>1 my) b methane clathrates 11 x103 limestone 60x106 (0.1 -1 y) (50100 y) Sedimentation 0. Y _ NPP Fig. 1. Global carbon reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in Gt (101' g) C and Gt C/yr. Turnover times (reservoir divided by largest flux to or from reservoir ) are in parenthe ses. To convert Gt C tomoles of C, multiply by 8.3 x 1010. Sedimentary carbonates and kerogen are the the largest carbon reservoirs, followed by marine dissolved inorganic car bon (DIC), soils, surface sediments, and the atmosphere. The living biomass reservoir is somewhat smaller than the atmo and respiration. spheric carbon reservoir and actively exchanges with the atmospheric reservoir through photosynthesis Global estimates of important fluxes or transfers between reservoirs are shown. Net primary production (NPP = gross is approximately equal in terrestrial and marine environments. NPP photosynthesis-respiration) respiration. New Produc tion = particulate organic carbon (POC) and dissolved organic carbon (DOC) exported from surface waters. Approxi mately 20% of the ocean NPP occurs in the coastal ocean; 80% of this is deposited in surface sediments. Turnover or residence times for the reservoirs range from >>106 yr for kerogen in the sediment reservoir to 103 -105 years for peats and soil carbon, to about 3 years for atmospheric CO2 and <1 year for ocean biomass. Because of its small size and relatively slow equilibration with the ocean reservoir, the atmospheric carbon reservoir is presently out of balance. The difference between atmospheric sources (deforestation and combustion) and sinks (annual atmospheric increment and the difference between ocean influx and efflux) is the "missing sink" of 1.8 Gt C/yr. The major long-term sink for carbon is burial in deep sea sediments. This removal of a small portion (0.1%) of annual NPP is responsible for oxygen in the Earth's atmosphere. Protection of photosynthetically fixed organic carbon from oxi dation by photosynthetic oxygen (respiration) has permitted accumulation of oxygen in the atmosphere and ocean over geologic time. The carbon cycle is completed by weathering of uplifted marine shales or by combustion of fossil fuels. October 1997 263 Pools in 1015moles O2 ,Fluxes in 1015moles 02 y', Organic pools as 02 equivalent, (turnover time) Atmosphere 37,000 (3.7My) Terrestrial Gross PP 9.2 y-1 Autotroph respiration 4.6 y-1' Ocean O NPP (OC)4.6 y-1 Short-lived biota (OC) 11 (50 y) + Long-livedbiota leri soil, peat Exchange (OC) 180 (1000 y); 140 y 140 Y' Surface Ocean 6 (22 d) a 0.4 0C)_ Fires, heterotrophic respiration 4.6 y-1; and volcanism -0.01 y' Weathering Fossil fuel combustion 0.58 y1 Sedimentary PP 4.3 y-1 3.9 y-I Respiration Deep Ocean (OC>) -0.4 y-I 219 (-500 y) rocks (OC) 106 Fossil fuel reserves 760 Reference: Gross Sedimentation (OC) Keeling, Najjar, Bender & Tans, 1993 -0.01 ' Fig. 2. Global oxygen reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in 10'5moles 02 and 10t moles 02 per year. Turnover times (reservoir divided by largest flux to or from reservoir) are in parentheses. To convert moles 02 to Tg 02, multiply by 3.2 x 10 1. The atmosphere is the largest oxygen reservoir and has the longest turnover time. The atmospheric oxygen reservoir is approximately 200-fold larger and the turnover time is >106 times longer than the next largest reservoirs, the ocean-dis solved oxygen reservoir and long-lived plants. The major source of oxygen is photosynthesis, but this is almost exactly balanced by respiration. Note that ocean sediments are shown as an oxygen source, because the long-term storage of or ganic carbon in ocean sediments prevents oxidation and allows accumulation of oxygen in the atmosphere. Pools and fluxes inTg N and Tg N y', Tg = 1012 g; (turnover times) Fixation Natural terrestrial 190 y-' Natural oceanic 40 y-' crops 40 y-1 Leguminous Chemical fertilizer 80 y-' Combustion 20 y-' Terrestrial Biomass 3.5x104 (50y) Soil 9.5 x 104 (-2000 Atmosphere N2: 3.9-4.0x109 (107 y) Fixed N: 1.3-1.4 x103 (-5 wk) N 20: 1.4x103 (1_y) River runoff 36 y Marine Biomass Plants: 3x102 y) Animals: References: Burns & Hardy, 1975; Jaffe, 1992; McElroy et al., 1976; Schlesinger & Hartley, 1992; Stedman & Shetter, 1983; Soderlund & Svensson, 1976; Galloway et al., 1995 Denitrification Natural terrestrial 147 y1 110 y-' Natural ocean Biomass burning 12 y-1 Industrial combustion 20 y Sediments 4.0x108 (107 y) Weathering 5 y 1.7x102 Ocean N : 2.2x107 N20: 2.0x104 I norglanic: 6x1 05 Organic: 2x105 Sedimentation (burial) 14 y-1 ( Fig. 3. Global nitrogen reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in Tg (10t2 g) N and Tg N/yr. Turnover times (reservoir divided by largest flux to or from reservoir) are in parenthe ses. To convert Tg N tomoles of N, multiply by 7.1 x 10?. As with oxygen, the atmosphere, which is 78% N2, is the largest nitrogen reservoir. Other gaseous nitrogen species im portant in ozone chemistry have short lifetimes and are of local importance. Nitrous oxide, an important long-lived green house gas, is photolyzed in the stratosphere.The thermodynamicallystable formof nitrogen in thepresence of oxygen is not N2, butNO3-.However, conversion of relatively inertN2 toother forms is limitedby themicrobially mediated nitrogen fixation rate,and fixed nitrogen is rapidly incorporatedinto living tissue.Note that theanthropogenicnitrogen fixation rate is about60% thatof natural fixation.Microbially mediated denitrificationcompletes thenitrogen cycle. The nitrogen bio mass reservoirsare based on carbon reservoirsand theC:N ratio. 264 Bulletin of theEcological Society of America Pools and fluxes Tg P, Tg = 1012g; * livingpools; (turnover times) Atmosphere 0.028 (0.006 y, 53 h) Land Biota *3000 (47.2 y) Jahnke, Rivers Reactive 1.7 - 2.5 y-1 Total 20 y-( 1992; Berner &5 (2a00 10cean System 9x104 (50,000 y) Surface 1994 (0-3 km)Ocean WY-1 P Mineable 10,000 Fertilizer m.7 xm04 12 y-' 42 y-' el) Ocean (3.0 km) (1500 y) \ t biota 140 (48 d) 1 58 Sediments 4xt09 (2xlhry) Sedimentation Reference: Jahnke, 1992; Berner & Rao, 1994 Fig. 4. Global in Tg given ses. To Note phosphorus (1012 g) P and convert that Tg P reservoirs, fluxes, and turnover times. Major Tg to moles the phosphorus of times Turnover P/yr. P, multiply cycle has no by divided (reservoir 3.2 x largest flux to or from and is restricted to solid sediments. Marine phosphorite deposits are mined and reintroduced biomass reservoirs are derived from the carbon cycle and C:P ratios. Atmosphere Continental Terrestrial dust 20 y-1 Biogenic 2.5 y-1f Volcanoes 10 y-' f 43 y-1 Deposition Soils & Land Biota 3 x 105 (8.6x103 y) 1.6 ) are liquid phases. and sink is burial in marine ties. The phosphorus pool sizes and fluxes are reservoir in parenthe 1010. component, atmospheric reservoirs are underlined, by 13 y-1 _ (8d) major activi Pools and fluxes inTg S and Tg S y', Tg = 1012g; (turnover times) Marine 24 y-1 Lakes & Rivers 300 (3y) River runoff 104 y-' \ The to the cycle by man's 3.2 (10 d) COS (5-1 Oy) Seasalt particles 140 y-1t I Biogenic 15-30 y-1 159 y-' Deposition Open Ocean ~~Ocean 1.3 x 109 (6.8Xl106 y) *Marine biota 30 (0.1 -1 y) Ocean Sediments\ 3 x 108 (4xl106 y) Sedimentation 135 Lithosphere Reference: Andreae, 1990; Bates et al., 1992; Charlson, Anderson &McDuff, 1992 2.4x1010 (burial) y-1 (1.8x108 y) Fig. 5. Natural (preindustrial) global sulfur reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in Tg (1012 g) S and Tg S/yr. Turnover times (reservoir divided by largest flux to or from reser voir ) are in parentheses. To convert Tg S tomoles of S, multiply by 3.1 x 1010. The lithosphere is the largest reservoir, with turnover times of approximately major consituent, and ocean sediments, where sulfide and sulfate are the major turnover times of >106 yr. Carbonyl sulfide (COS) is the longest lived gaseous sulfur compound. 109 yr. Ocean waters, where sulfate is a forms, have similar reservoir sizes and Large particulate fluxes of sea salt and terrestrial dust are added to theatmosphere,but theirabundance is restrictedto altitudesof <1 km. The particleshave residence times of days, close to rainout times, reflecting theircontrol by precipitation. Some volcanic emissions are injected into the stratosphere,where theyhavemuch longer residence times. Note that thenet preindustrialflux of sulfur (as sulfate aerosol) is from theocean to land. October 1997 265 Pools and fluxes inTg S and Tg S yr-, Tg (turnover times) Atmosphere Continental Terrestrial dust 20 y- t Biogenic 2.5 yr-' emission 93 y-1t Anthropogenic 10 y-1 t Volcanoes 65 y-1 Deposition 1.6 Marine 81 y-' 20 y-' (8d) 1012g; 3.2 (10 d) COS (5-1 0y) Seasalt particles 140 y-' t Biogenic 15-30 y-1I 231 y- f Deposition Lakes & Rivers Soils & Land Biota 3 x 105 (8.6x103 y) 300 (3y) River runoff 213 y-' Ocean x 109 (6.8xl106 y) ~~~~~1.3 Lithosphere\ 2.4 x 10'? (1 .8xl108 y)\ from lithosphere Consumption 72 y-1 Weathering Open Ocean *Marine biota 30 (1 y) 150 y-1 Sedimentation (burial) 135Y-1 Ocean Sediments 3x 108(4x106y) References: Andreae, 1990; Bates et al., 1992; Charlson, Anderson &McDuff, 1992 Fig. 6. Global sulfur reservoirs, fluxes, and turnover times (mid-1980s). Major reservoirs are underlined, pool sizes and fluxes are given in Tg (1012 g) S and Tg S/yr. Turnover times (reservoir divided by largest flux to or from reservoir ) are in parentheses. To convert Tg S tomoles S, multiply by 3.1 x 10t?. rates. Most sulfur is additions at mid-1980s This figure is the same as Fig. 5, but includes estimated anthropogenic added to the atmosphere as SO2 by combustion of sulfur-rich fossil fuels (coal, oil). The SO2 is subsequently oxidized and becomes sulfate aerosol, which is removed by precipitation. sulfate additions is reversal of the net flux of sulfur from land to sea. Note that one effect of anthropogenic fluxes Pool inTeramoles (1012 moles), moles y1 (turnover times) Rivers (150 Estuarine Sedimentation (gross) 5.6y- 9 x 104 surface <2 AM | 70 AM av deep 10-180gM o la(Biological 400 y) Ocean Atmosphere 0 ? (days) iM av) 80% tropical 20% temperate EoI - 5 y: ynet kBiological 0.6 y-1 in 1012 240 y-1 (days) ^\Production 120 y-1 \114.5 y-1 Deep 0.4 y1 Margins (months) Rain Rate Weathering 2 (106-109 y) Hydrothermal References: Tr6guer et al. 1995 Nelson et al. 1995 yssal Sedimentation 29.1 y Bhi Deposition 120 y-1 Dissolution p1Dsoltio 90.De0 83%Abyssal 17% Continental Dissolution 1Export pwelling T<,5 Sedimentation - (net) 6.1 y.1 C Dissolution (months-centuries) Fig. 7. Global silica reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in Tmol (1012moles) Si and Tmol Si/yr. Turnover times (reservoir divided by largest flux to or from reservoir ) are in pa rentheses. To convert Tmol Si to Tg Si, multiply by 3.6 x 102. im The silica cycle is restricted to solid and aqueous phases, as there are no gaseous silica compounds of geochemical portance.The silica cycle is dominatedby ocean processes. Silica releasedby continentalweathering is transportedin dis solved and colloidal form by rivers to the ocean, where themajor sink is euphotic zone uptake by planktonic diatoms and radiolariansat high latitudesand in the tropics, respectively. 266 Bulletin of theEcological Society of America Pools in 103 km3; fluxes inkm3 y (turnover times) Atmosphere 13 (0.0009%) 1O1,000 y-1 Polar Ice, Glaciers 29,000 (2.08%) (16,000 lakes Freshwater (9 d) 0 y) 40,000 y-l 125(0.009%) (1-100y) 71,000 y-' Rivers Saline lakes 104 (0.008%) 1.2 (0.00009%) (10-1 000 yl 40,000 y-I (12-20 d) 425,000 \ Soil moisture 67 (0.005%) y-I Ocean ~~~~~~1.37xl106 (97.61%) 385,000 (37000 y-I y) e (280 d) Groundwater (active) 4000 (0.29%) (300 y) References: Schlesinger, 1993; Murray, 1992 Fig. 8. Global water reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes are given in 103 km3, and fluxes are given in km3/yr. Pool sizes, expressed as percentages of the total water budget, are given in parenthe ses. Water is present on Earth in three phases-solid, all of these phases are present at some place in liquid, and gas-and the Earth's major water reservoirs. The ocean is the largest water reservoir, with over 97% of the Earth's water, followed by the glacial reservoir with 2%. Both have turnover times of approximately 10,000 years. Although only slightly larger than the river reservoir, water in the atmosphere, which accounts for only 0.0009% of the total budget, plays a very impor tant role inmaintaining Earth's habitability. Water vapor is the most important greenhouse gas, and is responsible for some 30?C of greenhouse warming. In addition, water' s unusually high heat capacity and latent heats of vaporization and fusion play an important role in heat storage and transport. All phases of atmospheric water play important roles in the Earth' s ra diation budget. Atmospheric processes are responsible Enteric fermentation 80 y' Biomass burning 55 yt Termites 20 y-t Landfills 40 y' Coal production 35 yt Gas production 40 yt Wetlands I115y' boreal 35 y' tropical 80 y' Rice Production 100 yt for transporting water from the ocean to land. Pools and fluxes inTg CH and Tg yr', Tg = 10129; COH (turnover time) Atmosphere 4800 (1.7 ppm, + 1% y-') (9.6 y) Photochemical oxidation 450 y' Oceans and Lakes 10 y1 t Soi consumption 40 y1 Hydrael____________ _107 5? y-I ? production 500 y-I - consumption 460 y- = 40 y' annual atmospheric increase Fossil sources 20% Modern biogenic sources 70-90% References: Cicerone &Oremland, 1988 Fung etal., 1991 Reeburgh, Whalen & Alperin, 1993 Fig. 9. Global methane reservoirs, fluxes, and turnover times. Major reservoirs are underlined, pool sizes and fluxes are given in Tg (1012 g) CH4 and Tg CH4/yr. Turnover times (reservoir divided by largest flux to or from reservoir ) are in pa rentheses. To convert Tg CH4 tomoles of C, multiply by 6.25 x 1010. The methane budget is <1% of the Earth's carbon budget. Methane is present in quantity in only three reservoirs on Earth: as natural gas associated with fossil fuel reservoirs, as hydrates or clathrates (a cage-like structure of water ice that containsmethane), and in the atmosphere,which is the smallest reservoir.Methane in the atmosphere is photochemically oxidized, and the recentlyobserved increase in atmosphericconcentrationsis a resultof an imbalancebetween sources and themajor sink, photochemicaloxidation.Research onmethane, an importantgreenhousegas, has focused on fluxes influ encing theatmosphere. October 1997 267
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