Ninth International Conference on Permafrost ... - IARC Research
Ninth International Conference on Permafrost ... - IARC Research
Ninth International Conference on Permafrost ... - IARC Research
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Spatial Variati<strong>on</strong> in CO 2Release from Arctic Tundra as a Result of <strong>Permafrost</strong>Thawing and Thermokarst DevelopmentHanna LeeDepartment of Botany, University of Florida, Gainesville, FL 32601-8526, USAEdward A.G. SchuurDepartment of Botany, University of Florida, Gainesville, FL 32601-8526, USAJas<strong>on</strong> G. VogelDepartment of Botany, University of Florida, Gainesville, FL 32601-8526, USAIntroducti<strong>on</strong>One of the biggest potential feedbacks to global climatechange from high latitude ecosystems may come from thawingof permafrost, which stores 30% of the total global terrestrialsoil organic carb<strong>on</strong> (SOC) (Gorham 1991). <strong>Permafrost</strong>thawing may accelerate decompositi<strong>on</strong> of soil organicmatter (SOM) and increase carb<strong>on</strong> dioxide (CO 2) emissi<strong>on</strong>s,which could lead to further climatic warming (Oechel et al.2000). In particular, thermokarst formati<strong>on</strong> in resp<strong>on</strong>se topermafrost thawing could change C cycling in high latitudeecosystems bey<strong>on</strong>d simple increases in temperature becauseit has unique effects <strong>on</strong> soil c<strong>on</strong>diti<strong>on</strong>s.When permafrost thaws and drains in ice-rich areas, itcreates localized surface subsidence called thermokarst(Jorgens<strong>on</strong> et al. 2001). The changes in the ground surfacetopography can induce variati<strong>on</strong>s in soil properties such assoil temperature, moisture c<strong>on</strong>tent, and nutrient availability(Chapin et al. 2000). Our objective was to determine howpermafrost thawing and thermokarst development affect SOMdecompositi<strong>on</strong> and ecosystem C exchange. We hypothesizedthat there will be a positive relati<strong>on</strong>ship between the degreeof ground subsidence and CO 2emissi<strong>on</strong>s from SOM.Materials and MethodsField siteThis study was established at the Eight Mile Lake (EML)tundra site located 5 miles outside of Denali Nati<strong>on</strong>al Park. Previouswork by Osterkamp and Romanovsky (1999) m<strong>on</strong>itoreddeep soil temperatures at this site to 27 m belowground for theprevious two decades and observed increased permafrost temperaturesand thermokarst development (Osterkamp 2007).Three sites were established at EML as an observati<strong>on</strong>alnatural gradient study based <strong>on</strong> the degree of thermokarstdevelopment. The observed gradient was divided into threecategories: Minimal Thaw, where typical tussock tundra appearsleast disturbed; Moderate Thaw, where thermokarstdevelopment started about 20 years ago; and Severe Thaw,where there were significant surface depressi<strong>on</strong>s. Based <strong>on</strong>1951 aerial photographs, thermokarst development at SevereThaw was estimated to be present for at least 50 years(Schuur et al. 2007).Defining microtopographyWe defined the degrees and patterns of depressi<strong>on</strong> createdby thermokarst using a topographic survey. Twelve transectswere established within a 50 m × 50 m plot at each of thethree sites, and 600 (±50) points were surveyed. The majorindependent variable was elevati<strong>on</strong> representing variati<strong>on</strong>in microtopography created by thermokarst; lower surfacesrepresent subsidence by thermokarst development.Establishing the plotsA 50 × 25 m subplot was established within the surveyedarea at each site. In each plot, 50 equally spaced points wereselected and surveyed again with a fine-scale GPS (Trimble5700) unit within the plot to relate microtopography to soiltemperature, moisture, active layer thickness, ecosystemrespirati<strong>on</strong>, and photosynthesis.Soil propertiesSoil temperature, volumetric water c<strong>on</strong>tent (VWC), andactive layer thickness were measured across the sites. Ahandheld soil temperature probe was used to measure soiltemperature at 10, 20, and 30 cm during the growing seas<strong>on</strong>.VWC was measured at 10 and 20 cm belowground usinga soil moisture reflectometer (Campbell Scientific CS616),and a 1/8 inch rod was used as a depth probe to measureactive layer thickness.Carb<strong>on</strong> emissi<strong>on</strong>sCO 2flux was quantified 4 times during the summer of 2006and 2007 at the peak of the growing seas<strong>on</strong> to measure netecosystem exchange of carb<strong>on</strong> using an IRGA (infrared gasanalyzer, LiCOR820) attached to a 40 × 40 × 40 cm plasticchamber. Both dark CO 2chamber measurement and lightmeasurement were taken covered with a reflecting cloth, , com-pletely intercepting light and uncovering the chamber. Darkmeasurements estimate the rate of carb<strong>on</strong> emissi<strong>on</strong>s fromecosystem respirati<strong>on</strong>, whereas light measurements estimatecarb<strong>on</strong> emissi<strong>on</strong>s from ecosystem respirati<strong>on</strong> as well as carb<strong>on</strong>uptake by photosynthesis. Differences between light and darkmeasurement served as an estimate of photosynthesis.AnalysesTo compare the effects of microtopography am<strong>on</strong>g sites,the plot level elevati<strong>on</strong>s were normalized to relative valueswithin each site and semivariograms and correlograms werecalculated to mathematically define the surface structure.A multiple regressi<strong>on</strong> with stepwise selecti<strong>on</strong> was used toobtain the best relati<strong>on</strong>ship between microtopography andmeasured soil and ecosystem properties.173