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Ninth International Conference on Permafrost ... - IARC Research

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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 torganic cover—most intensively enrich mineral horiz<strong>on</strong>swith organic matter. A similar trend was observed for thesuccessi<strong>on</strong> developing through the stage of dense forest.Thus, the influence of fires <strong>on</strong> soil carb<strong>on</strong> pools has a dualnature: in the first stages, “expected” dramatic reducti<strong>on</strong>of carb<strong>on</strong> pools in organic horiz<strong>on</strong>s and less expressed inmineral horiz<strong>on</strong>s; in the later stages, postpyrogenic effectof organic matter accumulati<strong>on</strong> <strong>on</strong> the mineral surface andOC enrichment of mineral horiz<strong>on</strong>s due to intense recoveryprocesses in the ecosystem.ReferencesTarabukina, V.G. & Savvinov, D.D. 1990. Influence of fires<strong>on</strong> cryogenic soils. Novosibirsk: 120 pp.Figure 3. Alterati<strong>on</strong> of OC densities in organic and mineral horiz<strong>on</strong>sin dependence to fire age and/or type of postpyrogenic successi<strong>on</strong>(for the legend see Fig. 2).I – c<strong>on</strong>secutive postpyrogenic development of larch open forestII – development through stage of dense larch forestdepressi<strong>on</strong>s (1–4 m in diameter) indicate an intersecti<strong>on</strong> ofice wedges, which partially melt when vegetati<strong>on</strong> is destroyedduring the fire. The soil profiles are str<strong>on</strong>gly disturbed bycryoturbati<strong>on</strong>s.Postpyrogenic successi<strong>on</strong>s of vegetati<strong>on</strong> and soils arecyclical. This fact provided an opportunity to estimatedynamics of soil features including organic carb<strong>on</strong> (OC)densities (in similar lithological and geomorphologicalc<strong>on</strong>diti<strong>on</strong>s) (Fig. 3).OC densities in mineral horiz<strong>on</strong>s were calculated for the50 cm layer. OC storage in organic horiz<strong>on</strong>s was estimatedfor its actual thickness. “Expected” postpyrogenic reducti<strong>on</strong>of OC density is most significant in organic horiz<strong>on</strong>s (from3.9 to 0.5 kg C/m 2 ). However, 60 years after the fire, OCdensity reached its initial values in larch open forest and evenexceeded initial values in a highly productive ecosystem ofdense larch forest (∆ = 1.7 kg C/m 2 ) with thick moss coverstimulating active peat accumulati<strong>on</strong>. Alterati<strong>on</strong> of OCdensities in mineral horiz<strong>on</strong>s is less evident. For the larchopen forest ecosystem 30 years after the fire, the reducti<strong>on</strong>was fixed (∆ = -1.6 kg C/m 2 ); however, at the next measuringpoint (60 years after the fire), an intensive increase has beenrevealed (∆ = 2.5 kg C/m 2 ). Such “unobvious” change wasprimarily induced by two factors: active layer thicknessand cryoturbati<strong>on</strong>s. According to our data, in a 30- to 60-year period after the fire, active layer thickness decreases,reaching its initial values; at this time cryoturbati<strong>on</strong>s reachthe highest intensity. Cryoturbati<strong>on</strong>s in the presence of twoc<strong>on</strong>diti<strong>on</strong>s—close permafrost table and already formed thick212

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