12.07.2015 Views

Ninth International Conference on Permafrost ... - IARC Research

Ninth International Conference on Permafrost ... - IARC Research

Ninth International Conference on Permafrost ... - IARC Research

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Ni n t h In t e r n at i o n a l Co n f e r e n c e o n Pe r m a f r o s t020Water c<strong>on</strong>tent, m 3 m -30.35 0.40 0.45 0.50AAggregate stability, %0 30 35 40 45B800.0700.0Air temperature increasedfrom -7 to + 2 ° CCO 2 c<strong>on</strong>c.40600.0Ambient CO 2 c<strong>on</strong>c.Soil depth, mm6080100120Figure 1. Soil water c<strong>on</strong>tents and aggregate stability in a relativelywet core of Portneuf silt loam after freezing at -7°C.(Fig. 1A). There was little change in water c<strong>on</strong>tent below 58mm. Lehrsch et al. (1991) found that water c<strong>on</strong>tent of 0.34m 3 m -3 in Portneuf silt loam was sufficient to decrease itsaggregate stability when it was frozen, then thawed. In thisstudy, at water c<strong>on</strong>tent nearly <strong>on</strong>e-third greater, structuralchanges will occur.Indeed, soil structure near the surface reflected the oftobservedinverse relati<strong>on</strong>ship between water c<strong>on</strong>tent andaggregate stability after freezing (Fig. 1B) (Lehrsch et al.1991). As water c<strong>on</strong>tent decreased with depth, aggregatestability increased from 35% at the 10 mm depth to 40%at the 33 mm depth, a 1.14-fold increase. In the middle ofthe core, however, aggregate stability changed little. Therelatively low aggregate stability near the bottom of thecore may have been a c<strong>on</strong>sequence of difficulty experiencedwhen dissecting the core prior to analysis.CO 2and N 2O emissi<strong>on</strong>sPreliminary data revealed that both CO 2and N 2Oc<strong>on</strong>centrati<strong>on</strong>s measured in the headspace above intact soilcores increased with time as <strong>on</strong>ce-frozen soil c<strong>on</strong>tainingaged manure thawed at +2°C (Fig. 2). CO 2c<strong>on</strong>centrati<strong>on</strong>sincreased by about 200 ppmv (37% greater than ambient)in the first 30 h after air temperatures in the envir<strong>on</strong>mentalchamber were increased from -7 to +2°C. For subsequentFTC and thawing temperatures of +2°C, CO 2emissi<strong>on</strong>s fromintact cores may not be as great. The C pool that provides thesubstrate for microbial producti<strong>on</strong> of CO 2as repeatedly frozensoils thaw is apparently limited in size, since Herrmann andWitter (2002) found that most CO 2was produced in the first4 FTC. Data in Figure 2 also reveal that N 2O c<strong>on</strong>centrati<strong>on</strong>safter <strong>on</strong>e incidence of freezing increased by about 5.7 ppmv(more than eight times greater than ambient) in the first 30 hafter thawing began. The c<strong>on</strong>centrati<strong>on</strong> of CO 2peaked about24 h, and N 2O peaked about 26 h after the temperature wasincreased (Fig. 2). Lysed microbial cells may have providedsubstrate for microbial denitrificati<strong>on</strong> (Sehy et al. 2004).Gas c<strong>on</strong>centrati<strong>on</strong>, ppmv500.010.07.55.02.50.0Ambient N 2 O c<strong>on</strong>c.0 5 20 25 30Elapsed time, hSummaryAvailable data indicate that FTC (1) caused soil water toredistribute and (2) interacted with water c<strong>on</strong>tent to alterthe near-surface aggregate stability of wet soil. Moreover,compared to ambient c<strong>on</strong>diti<strong>on</strong>s, emissi<strong>on</strong>s of CO 2increasedby a third, and N 2O increased by a factor of eight, eachpeaking 24 to 26 h after thawing began, from intact cores ofsoil frozen <strong>on</strong>ly <strong>on</strong>ce and thawed at <strong>on</strong>ly +2°C.ReferencesN 2 O c<strong>on</strong>c.Figure 2. CO 2and N 2O emissi<strong>on</strong>s as a functi<strong>on</strong> of thawing timefrom intact cores frozen <strong>on</strong>ce.Herrmann, A. & Witter, E. 2002. Sources of C and Nc<strong>on</strong>tributing to the flush in mineralizati<strong>on</strong> up<strong>on</strong> freezethawcycles in soils. Soil Biology & Biochemistry 34:1495-1505.Lehrsch, G.A. 1998. Freeze-thaw cycles increase nearsurfaceaggregate stability. Soil Science 163: 63-70.Lehrsch, G.A., Sojka, R.E., Carter, D.L. & Jolley, P.M. 1991.Freezing effects <strong>on</strong> aggregate stability affected bytexture, mineralogy, and organic matter. Soil ScienceSociety of America Journal 55: 1401-1406.Sehy, U., Dyckmans, J., Ruser, R. & Munch, J.C. 2004.Adding dissolved organic carb<strong>on</strong> to simulate freezethawrelated N 2O emissi<strong>on</strong>s from soil. Journal ofPlant Nutriti<strong>on</strong> and Soil Science 167: 471-478.van Bochove, E., J<strong>on</strong>es, H.G., Bertrand, N. & Prevost, D.2000. Winter fluxes of greenhouse gases from snowcoveredagricultural soil: Intra-annual and interannualvariati<strong>on</strong>s. Global Biogeochemical Cycles 14:113-125.176

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!