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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 tshrub layer, height up to 10 cm (Carex globularis, Vacciniumuliginosum); and (3) moss and lichen layer (Сladina stellaris,Polytrichum strictum, Sphagnum fuscum).On a frost mound repeatedly disturbed in 2004 as a resultof rec<strong>on</strong>structi<strong>on</strong> of the gas pipeline, vegetati<strong>on</strong> cover is rare;also it is composed of a small number of species. Vegetati<strong>on</strong>recovery here begins in places where surface peat was kept.More than half of the disturbed plot is flooded with wateras a result of infringement of superficial drain by the gaspipeline embankment.On the natural plot, relative elevati<strong>on</strong>s reach 160 cm, and<strong>on</strong> the disturbed plot, they reach 280 cm due to settlementand flooding of the large part of the plot.On plot measurements of soil temperature, surface anddepth of 20 cm have been carried out. The maps are compiled<strong>on</strong> the basis of the given temperatures. On the undisturbedfrost mound, the maximal temperature of a surface was14.5°С, <strong>on</strong> depth 20 cm, -9.7°С; the minimal temperature<strong>on</strong> a surface was 6.3°С, <strong>on</strong> the depth 20 cm, -2.7°С. On thedisturbed plot, the maximal soil temperature at the depth of20 cm has increased up to 16°С <strong>on</strong> peat sites, before coveredwith lichen, and minimal temperature was 9.5°С. Rise in thesoil temperature has made 7°С <strong>on</strong> the average. Change oftemperature influences formati<strong>on</strong> of vegetative cover, theabove soil temperature, the more variously specific structureof vegetati<strong>on</strong> <strong>on</strong> the given site.Analysis of the given measurements of thaw depth <strong>on</strong> siteshas shown the following: Thaw depth <strong>on</strong> the undisturbed frostmound was more <strong>on</strong> the raised sites, occupied with denseLabrador tea; in the space between hummocks occupiedwith moss-lichen vegetati<strong>on</strong>, thaw depth was less.The maximal thaw depth was 180 cm; the minimal thawdepth (50 cm) is marked in the frozen crack with lichencover. According to supervised data, the map of active layerthickness <strong>on</strong> the undisturbed site is compiled (Fig. 2).On the disturbed plot, the permafrost table has g<strong>on</strong>e downto a depth of 10 and more meters, according to geophysicalworks (P<strong>on</strong>omareva & Skvortsov 2006).Measurements of peat thickness have shown that thethickness of peat <strong>on</strong> a plot changes c<strong>on</strong>siderably; it varies inlimits from 5 up to 65 cm, depending <strong>on</strong> the microrelief andvegetati<strong>on</strong> cover. The least thickness of peat is observed <strong>on</strong>equal sites <strong>on</strong> which the sedge grows. The greatest thicknessof peat is characteristic for peat moss hummocks withcloudberries.Human-induced disturbances at c<strong>on</strong>structi<strong>on</strong> and operati<strong>on</strong>of the gas pipeline Nadym-Punga in West Siberia renderedsignificant influence <strong>on</strong> the vegetati<strong>on</strong> cover and otherecosystem comp<strong>on</strong>ents, which changes are reflected in thecomplete compiled maps.These maps can be used for compiling prognostic andecological maps and also for planning acti<strong>on</strong>s related toenvir<strong>on</strong>ment c<strong>on</strong>servati<strong>on</strong>.AcknowledgmentsI thank my colleagues from Earth Cryosphere InstituteO.E. P<strong>on</strong>omareva, O.L. Opokina, and E.V. Elantsev for helpwith the fieldwork.This study was made possible through financial supportfrom the grant of Tyumen governor and the U.S. Nati<strong>on</strong>alScience Foundati<strong>on</strong> (Grants OPP-9732051 and OPP-0225603).ReferencesBliss, L.C. 1975. Dev<strong>on</strong> Island, Canada. Ecolog. Bull. 20:17-60.Bocher, T.W. 1949. Climate, soil and lakes in c<strong>on</strong>tinentalWest Greenland in relati<strong>on</strong> to plant life. Medd. omGr<strong>on</strong>land, Bd. 147 (N2,1949): 4.Broll, G., Tarnocai, C. & Gould, J. 2003. L<strong>on</strong>g-term highArctic ecosystem m<strong>on</strong>itoring in Quttnir paag Nati<strong>on</strong>alPark, Ellesmere island, Canada. Proceedings of theEighth <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Permafrost</strong>,Zurich, Switzerland, July 21–25 2003, 1: 85-94.Koloskov, P.I. 1925. Climatic Foundati<strong>on</strong>s of Agriculturein the Amur Area. Blagoveshensk: Soviet for EasternMeteorological Service, 152 pp.Moskalenko N.G. (ed.) 2006. Anthropogenic changesof ecosystems in West Siberian gas province. M.,RASHN, 358.P<strong>on</strong>omareva, O.E. & Skvotsov, A.G. 2006. Methods andresults of exogenous geological process study inNadym regi<strong>on</strong> of West Siberia. Proceedings of the<str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g>. Tyumen, TGNGU. 1: 272-274.Rannie, W.F. 1986. Summer air temperature and numberof vascular species in arctic Canada. Arctic 39: 133-137.Timin, M.E., Coller, B.D., Zich, J. & Walker, D.A. 1973. Acomputer simulati<strong>on</strong> of the arctic tundra ecosystemnear Borrow, Alaska. In: US Tundra Biome Rep. SanDiego State Univ. (73-1): 1-82.Walker, D.A. 1985. Vegetati<strong>on</strong> and Envir<strong>on</strong>mental Gradientsof the Prudhoe Bay Regi<strong>on</strong>, Alaska. Hanover, 239pp.Figure 2. Seas<strong>on</strong>al thaw depth <strong>on</strong> undisturbed frost mound (cm).128

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