Ungulate vs. Landscape Control of Soil C and N Processes in Grasslands of Yellowstone National Park
1998; Wiley; Volume: 79; Issue: 7 Linguagem: Inglês
10.2307/176818
ISSN1939-9170
AutoresDouglas A. Frank, Peter M. Groffman,
Tópico(s)Plant Ecology and Soil Science
ResumoEcologyVolume 79, Issue 7 p. 2229-2241 Article UNGULATE VS. LANDSCAPE CONTROL OF SOIL C AND N PROCESSES IN GRASSLANDS OF YELLOWSTONE NATIONAL PARK Douglas A. Frank, Douglas A. Frank Biological Research Laboratories, Syracuse University, Syracuse, New York 13244-1220 USASearch for more papers by this authorPeter M. Groffman, Peter M. Groffman Institute of Ecosystem Studies, Box AB, Millbrook, New York 12545-0129 USASearch for more papers by this author Douglas A. Frank, Douglas A. Frank Biological Research Laboratories, Syracuse University, Syracuse, New York 13244-1220 USASearch for more papers by this authorPeter M. Groffman, Peter M. Groffman Institute of Ecosystem Studies, Box AB, Millbrook, New York 12545-0129 USASearch for more papers by this author First published: 01 October 1998 https://doi.org/10.1890/0012-9658(1998)079[2229:UVLCOS]2.0.CO;2Citations: 257Read the full textAboutPDF ToolsRequest permissionExport citationAdd to favoritesTrack citation ShareShare Give accessShare full text accessShare full-text accessPlease review our Terms and Conditions of Use and check box below to share full-text version of article.I have read and accept the Wiley Online Library Terms and Conditions of UseShareable LinkUse the link below to share a full-text version of this article with your friends and colleagues. Learn more.Copy URL Abstract Within large grassland ecosystems, climatic and topographic gradients are considered the primary controls of soil processes. Ungulates also can influence soil dynamics; however the relative contribution of large herbivores to controlling grassland soil processes remains largely unknown. In this study, we compared the effects of native migratory ungulates and variable site ("landscape") conditions, caused by combined climatic and topographic variability, on grassland of the northern winter range of Yellowstone National Park by determining soil C and N dynamics inside and outside 33–37 yr exclosures at seven diverse sites. Sites included hilltop, slope, and slope bottom positions across a climatic gradient and represented among the driest and wettest grasslands on the northern winter range. We performed two experiments: (1) a 12-mo in situ net N mineralization study and (2) a long-term (62-wk) laboratory incubation to measure potential N mineralization and microbial respiration. Results from the in situ experiment indicated that average net N mineralization among grazed plots (3.8 g N·m−2·yr−1) was double that of fenced, ungrazed plots (1.9 g N·m−2·yr−1). Mean grazer enhancement of net N mineralization across sites (1.9 g N·m−2·yr−1) approached the maximum difference in net N mineralization among fenced plots (2.2 g N·m−2·yr−1), i.e., the greatest landscape effect observed. Furthermore, ungulates substantially increased between-site variation in mineralization; grazed grassland, 1 sd = 2.2 g N·m−2·yr−1, fenced grassland, 1 sd = 0.85 g N·m−2·yr−1. In the long-term incubation, potential microbial respiration and net N mineralization were positively related to total soil C and N content, respectively. There was greater variation in potential respiration and net N mineralization early in the incubation, when labile material was processed, compared to late in the incubation, when more recalcitrant substrate was processed, suggesting that between-site variation in labile organic matter was greater than that of recalcitrant material. Herbivores improved the organic matter quality of soil, increasing the labile fractions and reducing the recalcitrant fractions. Grazers reduced C respired/N mineralized ratios, an index of microbial N immobilization, by an average of 21%. However, the largest landscape influence on the immobilization index was 13-fold greater than the grazer effect. Given that the greatest landscape influence on in situ net mineralization (2.2 g N·m−2·yr−1) was similar to the average grazer impact on that rate (1.9 g N·m−2·yr−1), we hypothesize that the landscape effect on field N availability was primarily caused by variation in microbial immobilization, while the grazing effect was primarily due to stimulation of gross mineralization. These results indicate that the relative importance of ungulates in controlling soil N cycling may be more important than previously suspected for grasslands supporting large herds of migratory ungulates, and that the dominant mechanisms underlying the landscape and ungulate influences on soil mineral fluxes may differ. Literature Cited Aandahl, A. R. 1948. The characterization of slope positions and their influence on total nitrogen content of a few virgin soils of western Iowa. Soil Science Society of America Proceedings 13: 449– 454. Burke, I. C. 1989. Control of nitrogen mineralization in a sagebrush steppe landscape. Ecology 70: 1115– 1126. Burke, I. C., W. A. Reiners, and D. S. Schimel . 1989. Organic matter turnover in a sagebrush steppe landscape. Biogeochemistry 7: 11– 31. Caldwell, M. M., J. H. Richards, D. A. Johnson, R. S. Nowak, and R. S. Dzurec . 1981. Coping with herbivory: photosynthetic capacity and resource allocation in two semiarid Agropyron bunchgrasses. Oecologia 50: 14– 24. Charley, J. L., and N. E. West . 1977. Micro-patterns of nitrogen mineralization activity in soils of some shrub-dominated semi-desert ecosystems of Utah. Soil Biology and Biochemistry 9: 357– 365. Coppock, D. L., J. K. Detling, J. E. Ellis, and M. I. Dyer . 1983. Plant–herbivore interactions in a North American mixed grass prairie. I. Effects of black-tailed prairie dogs on intraseasonal plant biomass and nutrient dynamics and plant species diversity. Oecologia 56: 1– 9. Coughenour, M. B. 1991. Biomass and nitrogen responses to grazing of upland steppe in Yellowstone's northern winter range. Journal of Applied Ecology 28: 71– 82. Day, T. A., and J. K. Detling . 1990. Grassland patch dynamics and herbivore grazing preference following urine deposition. Ecology 71: 180– 188. Eno, C. F. 1960. Nitrate production in the field by incubating the soil in polyethylene bags. Soil Science Society of America Proceedings 24: 277– 179. Floate, M. J. S. 1981. Effects of grazing by large herbivores on nitrogen cycling in agricultural systems. In F. E. Clark and T. Rosswall, editors. Terrestrial nitrogen cycles. Ecological Bulletins-NFR 33: 585– 601. Frank, D. A., and R. D. Evans . 1997. Effects of native grazers on grassland N cycling in Yellowstone National Park. Ecology 78: 2238– 2248. Frank, D. A., R. S. Inouye, N. Huntly, G. W. Minshall, and J. E. Anderson . 1994. The biogeochemistry of a north-temperate grassland with native ungulates: nitrogen dynamics in Yellowstone National Park. Biogeochemistry 26: 163– 188. Frank, D. A., and S. J. McNaughton . 1992. The ecology of plants, large mammalian herbivores, and drought in Yellowstone National Park. Ecology 73: 2043– 2058. Frank, D. A., and S. J. McNaughton . 1993. Evidence for the promotion of aboveground grassland production in Yellowstone National Park. Oecologia 96: 157– 161. Hobbie, S. E. 1992. Effects of plant species on nutrient cycling. Trends in Ecology and Evolution 7: 336– 339. Hobbie, S. E. 1996. Temperature and plant species control over litter decomposition in Alaskan tundra. Ecological Monographs 66: 503– 522. Hobbs, N. T. 1996. Modification of ecosystems by ungulates. Journal of Range Management 60: 695– 713. Holland, E. A., and J. K. Detling . 1990. Plant response to herbivory and belowground nitrogen cycling. Ecology 71: 1040– 1049. Holland, E. A., W. J. Parton, J. K. Detling, and D. L. Coppock . 1992. Physiological responses of plant populations to herbivory and their consequences for ecosystem nutrient flow. American Naturalist 140: 685– 706. Houston, D. B. 1982. The northern Yellowstone elk: ecology and management. Macmillan, New York, New York, USA. Huntly, N. 1991. Herbivores and the dynamics of communities and ecosystems. Annual Review of Ecology and Systematics 22: 477– 503. Ingham, R. E., and J. K. Detling . 1984. Plant–herbivore interactions in a North American mixed-grass prairie. III. Soil nematode populations and root biomass on Cynomys ludovicianus colonies and adjacent uncolonized areas. Oecologia 63: 307– 313. Jameson, D. A. 1963. Responses of individual plants to harvesting. Botanical Review 29: 532– 594. Jaramillo, V. J., and J. K. Detling . 1992. Small-scale heterogeneity in a semi-arid North American grassland. I. Tillering, N uptake and retranslocation in simulated urine patches. Journal of Applied Ecology 29: 1– 8. Jenny, H. 1941. Factors of soil formation. McGraw-Hill, New York, New York, USA. Jones, R. L., and H. C. Hanson . 1985. Mineral licks, geophagy, and biogeochemistry of North American ungulates. Iowa State University Press, Ames, Iowa, USA. Keefer, W. R. 1987. The geological story of Yellowstone National Park. Yellowstone Library and Museum Association, Mammoth, Wyoming, USA. Klopatek, J. M. 1987. Nitrogen mineralization and nitrification in mineral soils of pinyon–juniper ecosystems. Soil Science Society of America Journal 51: 453– 457. Köchy, M., and S. D. Wilson . 1997. Litter decomposition and nitrogen dynamics in aspen forest and mixed-grass prairie. Ecology 78: 732– 739. Lajtha, K., and W. H. Schlesinger . 1986. Plant response to variations in nitrogen availability in a desert shrubland community. Biogeochemistry 2: 29– 38. Malo, D. D., B. K. Worcester, D. K. Cassel, and K. D. Matzdorf . 1974. Soil–landscape relationships in a closed drainage system. Soil Science Society of America Proceedings 38: 813– 818. McNaughton, S. J. 1985. Ecology of a grazing ecosystem: the Serengeti. Ecological Monographs 55: 259– 295. McNaughton, S. J. 1990. Mineral nutrition and seasonal movement of African migratory ungulates. Nature 334: 343– 345. McNaughton, S. J., F. F. Banyikwa, and M. M. McNaughton . 1997. Promotion of the cycling of diet-enhancing nutrients by African grazers. Science 278: 1798– 1800. McNaughton, S. J., and N. J. Georgiadis . 1986. Ecology of African grazing and browsing mammals. Annual Review of Ecology and Systematics 17: 39– 65. McNaughton, S. J., R. W. Ruess, and S. W. Seagle . 1988. Large mammals and process dynamics in African ecosystems. BioScience 38: 794– 800. Meentemeyer, V. 1978. Macroclimate and lignin control of decomposition. Ecology 59: 465– 472. Miller, R. F., and J. A. Rose . 1992. Growth and carbon allocation of Agropyron desertatum following autumn defoliation. Oecologia 89: 482– 486. Nadelhoffer, K. J. 1990. Microlysimeter for measuring nitrogen mineralization and microbial respiration in aerobic soil incubations. Soil Science Society of America Journal 54: 411– 415. Norland, J. E., L. R. Irby, and C. B. Marlow . 1985. Determination of optimum bison stocking rate in Theodore Roosevelt National Park, North Dakota. Journal of Environmental Management 21: 225– 239. Parton, W. J., D. S. Schimel, C. V. Cole, and D. S. Ojima . 1987. Analysis of factors controlling soil organic matter levels in the Great Plains grasslands. Soil Science Society of America Journal 51: 1173– 1179. Parton, W. J., J. W. B. Stewart, and C. V. Cole . 1988. Dynamics of C, N, P and S in grassland soils: a model. Biogeochemistry 5: 109– 131. Pastor, J., B. Dewey, R. J. Naiman, P. F. McInnes, and Y. Cohen . 1993. Moose browsing and soil fertility in the boreal forests of Isle Royale National Park. Ecology 74: 467– 480. Paul, E. A., and F. E. Clark . 1989. Soil microbiology and biochemistry. Academic Press, New York, New York, USA. Richards, J. H. 1984. Root growth response to defoliation in two Agropyron bunchgrasses: field observations with an improved root periscope. Oecologia 64: 21– 25. Risser, P. J., and W. J. Parton . 1982. Ecosystem analysis of the tallgrass prairie: nitrogen cycle. Ecology 63: 1342– 1351. Ruess, R. W., and S. W. Seagle . 1994. Landscape patterns in soil microbial processes in the Serengeti National Park, Tanzania. Ecology 75: 892– 904. Schimel, D. S. 1986. Carbon and nitrogen turnover in adjacent grassland and cropland systems. Biogeochemistry 2: 345– 357. Schimel, D. S., D. C. Coleman, and K. A. Horton . 1985a.. Soil organic matter dynamics in paired rangeland and cropland toposequences in North Dakota. Geoderma 36: 201– 214. Schimel, J. P., K. Kielland, and F. S. Chapin III . 1996. Nutrient availability and uptake by tundra plants. Pages 203–221 in J. F. Reynolds and J. D. Tenhunen, editors. Springer-Verlag, New York, New York, USA. Schimel, D. S., M. A. Stillwell, and R. G. Woodmansee . 1985b.. Biogeochemistry of C, N, and P on a catena of the shortgrass steppe. Ecology 66: 276– 282. Schlesinger, W. H., J. F. Reynolds, G. L. Cunningham, L. F. Huenneke, W. M. Jarrell, R. A. Virginia, and W. G. Whitford . 1990. Biological feedbacks in global desertification. Science 247: 1043– 1048. Seagle, S. W., and S. J. McNaughton . 1992. Spatial variation in forage nutrient concentrations and the distribution of Serengeti grazing ungulates. Landscape Ecology 7: 229– 241. Seastedt, T. R. 1985. Maximization of primary and secondary productivity by grazers. American Naturalist 126: 559– 564. Seastedt, T. R., R. A. Ramundo, and D. C. Hayes . 1988. Maximization of densities of soil animals by foliage herbivory: empirical evidence, graphical, and conceptual models. Oikos 51: 243– 248. Senft, R. L., M. B. Coughenour, D. W. Bailey, L. R. Rittenhouse, O. E. Sala, and D. M. Swift . 1987. Large herbivore foraging and ecological hierarchies. BioScience 37: 789– 799. Shariff, A. R., M. E. Biondini, and C. E. Grygiel . 1994. Grazing intensity effects on litter decomposition and soil nitrogen mineralization. Journal of Range Manangement 47: 444– 449. Singer, F. J., and J. A. Mack . 1993. Potential ungulate prey for gray wolves. Pages 75–117 in R. S. Cook, editor. Ecological issues on reintroducing wolves into Yellowstone National Park. Scientific Monograph NPS/NRYELL/NRSM-93/22. United States Department of Interior, Washington, D.C., USA. Stanford, G., and S. J. Smith . 1972. Nitrogen mineralization potentials of soils. Soil Science Society of America Proceedings 36: 465– 472. Taylor, R. J. 1984. Foraging in the eastern grey kangaroo and wallaroo. Journal of Animal Ecology 53: 65– 74. Tilman, D. 1988. Plant strategies and the dynamics and structure of plant communities. Monographs in Population Biology 26. Princeton University Press, Princeton, New Jersey, USA. Tracy, B. F., and S. J. McNaughton . 1995. Elemental analysis of mineral lick soils from the Serengeti National Park, the Konza Prairie and Yellowstone National Park. Ecography 18: 91– 94. Turner, C. L., J. M. Blair, R. J. Schartz, and J. C Neel . 1997. Soil N and plant responses to fire, topography, and supplemental N in tallgrass prairie. Ecology 78: 1832– 1843. Turner, M. G., and S. P. Bratton . 1987. Fire, grazing, and the landscape heterogeneity of a Georgia barrier island. Pages 85–101 in M. G. Turner, editor. Landscape heterogeneity and disturbance. Springer-Verlag, New York, New York, USA. Valentine, K. A. 1947. Distance from water as a factor in grazing capacity of rangeland. Journal of Forage Science 45: 749– 754. Vázquez de Aldana, B. R., M. E. Pérez Corona, A. García Ciudad, and B. García Criado . 1996. Mineral content in semiarid grassland systems as affected by community structure and soil characteristics. Acta Œcologica 17: 245– 259. Vitousek, P. M., and R. W. Howarth . 1991. Nitrogen limitation on land and in the sea: how can it occur? Biogeochemistry 13: 87– 115. Weaver, J. E., and E. Zink . 1946. Some effects of season, habitat, and clipping on the chemical composition of Andropogon furcatus and Stipa spartea.. Botanical Gazette 107: 427– 441. Wedin, D. A., and J. Pastor . 1993. Nitrogen mineralization dynamics in grass monocultures. Oecologia 96: 186– 192. Wedin, D. A., and D. Tilman . 1990. Species effects on nitrogen cycling: a test with perennial grasses. Oecologia 84: 433– 441. Woodmansee, R. G. 1978. Additions and losses of nitrogen in grassland ecosystems. BioScience 28: 448– 453. Citing Literature Volume79, Issue7October 1998Pages 2229-2241 ReferencesRelatedInformation
Referência(s)