DIFFERENCES IN SOIL RESPIRATION RATES BASED ON VEGETATION TYPE Maggie Vest Winter Ecology 2013 Mountain Research Station Introduction Estimated 20% of the annual soil respiration occurs during the winter. Estimates range from 3% to 50% (Hobbie et al. 2000). High variability across small spatial scales (Scott-Denton et al. 2002). Lack of understanding of the controlling factors in mid- and high-latitude systems (Hobbie et al. 2000). Soil temperature is the best predictor for soil respiration (Scott-Denton et al. 2002). Vegetation and Soil Respiration Connection between vegetation type and soil respiration at the landscape scale (Grogan 2012). Total CO2 flux ranged from 34 to 126g CO2/C m^2 for various vegetation types in the low arctic tundra in Canada. Ecosystem-specific interactions between snow depth, vegetation cover, moisture, and litter production also affect CO2 flux Different decomposition rates between evergreens and deciduous trees (Hobbie et al. 2000). Hypothesis The aim of this study is to determine the degree of significance that surrounding vegetation has on soil respiration during wintertime. Question: Does the surrounding vegetation significantly impact soil respiration rates in the subalpine forests? Hypothesis: Deciduous trees are likely to have higher rates of soil respiration than conifers. Methods 3 vegetation types Aspen Lodgepole Spruce 3 Replicates for each site Trees with 30cm< snow depth Measured CO2 concentrations over a 2 minute period Recorded site features: temperature of soil surface, snow depth, soil moisture, amount of organic litter, litter composition Results Aspen-Lodgepole P Value: 0.11 Aspen-Spruce P Value: 0.46 Lodgepole-Spruce P Value: 0.10 Other Factors Affecting Soil Respiration Snow Depth Snow Depth versus Vegetation Aspen y = 3E-23x14.01 R² = 0.999 P Value=0.02 0.5 0.45 0.4 Lodgepole y = 0.761ln(x) - 2.429 R² = 0.787 P Value= 0.31 CO2 Flux (ppm) 0.35 0.3 0.25 0.2 0.15 0.1 0.05 0 30 32 34 36 38 Snow Depth (cm) 40 42 44 Spruce y = 0.658ln(x) - 2.191 R² = 0.123 P Value= 0.77 Aspen Lodgepole Spruce Power (Aspen) Log. (Lodgepole) Log. (Spruce) Other Factors Affecting Soil Respiration Soil Temperature Lodgepole Aspen y = 0.055x 0.150x + 0.441 0.940 R² = 0.951 0.869 P Value= 0.14 0.24 Soil Temperature versus Vegetation 0.5 0.45 0.4 CO2 Flux (ppm) 0.35 0.3 0.25 Spruce y = -0.103x - 0.228 R² = 0.548 P Value= 0.47 Aspen 0.2 0.15 0.1 Lodgepole 0.05 Spruce 0 -6 -5 -4 -3 Temperature (C) -2 -1 0 Other Factors Affecting Soil Respiration Ground Litter Organic Litter versus Vegetation 0.5 Aspen y = 0.000x5.469 R² = 0.975 P Value= 0.10 0.45 0.4 CO2 FLux (ppm) 0.35 Lodgepole y = 0.024x2.025 R² = 0.870 P Value= 0.23 0.3 0.25 Spruce y = 0.091x0.594 R² = 0.485 P Value= 0.51 0.2 0.15 0.1 Aspen Lodgepole Spruce 0.05 0 1 2 3 Scale of Organic Litter 4 Results Overall results were insignificant Aspen CO2 flux and snow depth were only significant data Results suggest expected trends of aspens having higher soil respiration than the evergreens Discussion Vegetation potentially impacts the rate of soil respiration Errors Short time scale of project Small sample size Further research is needed in order to determine the degree of significance that vegetation has on soil respiration rates. Summary Winter time soil respiration has the potential to significantly impact the annual net carbon balance (Grogan 2012). Results suggest expected trends of aspens having higher soil respiration than the evergreens. Further research is needed in order to determine the degree of significance that vegetation has on soil respiration rates. Acknowledgements Thank to Rob for being a field partner Thanks to Tim, Derek, and the CU Mountain Research Center The End References Brooks, Paul D., S. K. Schmidt, and M. W. Williams. 1997. Winter production of CO2 and N2O from alpine tundra: environmental controls and relationship in inter-system C and N fluxes. Oecologia 110: 403-413. Grogan, Paul. 2012. Cold season respiration across a low arctic landscape: the influences of vegetation type, snow depth, and interannual climatic variation. Arctic, Antarctic, and Alpine Research 44:446-456. 1938-4246-44.4.446. Hobbie, Sarah E., J. P. Schimel, S. E. Trumbore, and J. R. Randersons. 2000. Controls over carbon storage and turnover in high-latitude soils. Global Change Biology 6:196-210. Scott-Denton, Laura, K. L. Sparks, R. K. Monson. 2003. Spatial and temporal controls of soil respiration rate in a high-elevation, subalpine forest. Soil Biology and Biochemistry 35: 525-534. Schadt, Christopher, M. P. Martin, D. A. Lipson, S. K. Schmidt. 2003. Seasonal Dynamics of previously unknown fungal lineages in tundra soils. Science 302: 1359-1361. Tuomi, M, T. Thum, H. Jarvinen, S. Fronzek, B. Berg, M. Harmon, J. A. Trofymow, S. Sevanto, J. Liski. 2009. Leaf litter decomposition-estimates of global variability based on Yasso07 model. Ecological Modeling 220: 3362-3371. Appendix CO2 Flux Site 1 y = 0.036x + 468.7 R² = 0.871 P Value= 0.23 480 CO2 (ppm) 470 Site 2 y = 0.270x + 437.7 R² = 0.990 P Value= 0.06 460 450 Site 3 y = 0.405x + 428 R² = 0.997 P Value= 0.03 440 430 700 20 70 Site 2 y = 0.357x + 413.7 R² = 0.993 P Value= 0.05 Site 3 y = 0.463x + 556.9 R² = 0.997 P Value= 0.03 500 400 300 200 100 Lodgepole Site 1 0 Aspen Site 2 120 Time (seconds) R² = 0.996 P Value= 0.04 600 Aspen Site 1 420 -30 20 70 Time (seconds) Aspen Site 3 Spruce CO2 Flux CO2 (ppm) -30 Site 1 Lodgepole CO2 Flux y = 0.227x + 424.6 CO2 (ppm) Aspen CO2 Flux -30 Site 1 y = 0.081x + 506.1 R² = 0.895 P Value= 0.21 520 515 510 505 500 495 490 485 480 475 470 Site 2 y = 0.238x + 476.6 R² = 0.982 P Value= 0.10 Site 3 y = 0.130x + 475.7 R² = 0.912 P Value=0.09 Spruce Site 1 20 70 Time (seconds) 120 Spruce Site 2 Spruce Site 3 120 Lodgepole Site 2 Lodgepole Site 3 Appendix Results