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: http://eco.soil.msu.ru/acidification/index.html
Дата изменения: Mon Jan 16 21:00:38 2012 Дата индексирования: Mon Oct 1 23:45:59 2012 Кодировка: Windows-1251 |
Present choice |
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in ENGLISH на английском |
на РУССКОМ in Russian |
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Dr. Galina Koptsik | |||
Faculty of Soil Science, Moscow State University | |||
for addresses click on the arrow |
Participants:
Dr. Serguei Koptsik, Physics Faculty, Moscow State University
Dr. Ludmila Morgun, All-Russian Institute on Nature Conservation
Post-graduate Maria Zhuravleva, Soil Science Faculty, Moscow State University
Post-graduate Svetlana Livantsova, Soil Science Faculty, Moscow State University
Post-graduate Olga Gorlenko, Soil Science Faculty, Moscow State University
M.Sc. Raisa Okuneva, Soil Science Faculty, Moscow State University
The main objectives of the research project were to study soil-acid deposition interactions in forest ecosystems in European Russia. Present soil chemistry was considered for a number of forest soils. The interaction of various forest soils with different types of acidifying pollutants at different pollution regimes was studied both in field and laboratory experiments. Forest soil response to acid deposition, in particular the significance of soil organic matter in the processes of proton consumption, sulphur retention, aluminium and heavy metals mobilisation was investigated. Different approaches for estimation of forest soil sustainability to acid deposition, their advantages and limitations were compared. Computer simulation was used for describing soil acidification and critical load assessment. Critical loads of acid deposition and their exceedances were estimated and mapped for forest ecosystems of European Russia. Long-term response of forest soils to different deposition scenarios was evaluated.
Concurrent to the project objectives four major activities can be distinguished as described below.
For detailed results see publications.
Three pollution types were examined:
Near the local pollution sources field studies will be carried out at the plots situated along pollution gradient and characterised by similar parent rocks, soil compositions and relief positions. According to prevailing pollutants, the content of S and heavy metals (Ni, Cu, Co etc.) will be measured. A wide range of soil properties will be estimated, among them acidity, the content of exchangeable cations, buffer capacity, the content and composition of organic matter, S containing substances, heavy metals (exchangeable, ammonia acetate-soluble and acid-soluble forms, and total content).
Both natural and anthropogenic factors determine high acidity and low content of exchangeable base cations in thin sandy podzols subjected to airborne pollution from the Pechenganikel smelter. The deep penetration of acidity and depletion of base cations from the topsoil seems to reflect the early stages of ongoing soil acidification within 30-40 km from the pollution source. The complex character of soil variable changes is connected with a variety of structural and functional relationships within and across ecosystems as well as with a high natural variability.
Laboratory experiments included simulation of sulphate, heavy metals and combined pollution of different intensity. Soil columns reconstructed podzol profiles and included the organic and mineral horizons from O to BC. The columns were watered by solutions with different acidity several times per month during one year. Column leachates and soil samples after the end of the experiment were analysed for organic C, S, base cations, heavy metal content and pH; element balances for every soil horizon were estimated.
The simulated rain at pH 4.5 did not alter chemical properties of soils and soil solutions. As much as 95-99% of the applied protons were retained by soils and appeared in the percolates after a treatment period that depended on acid load and soil thickness. Ca and Mg in soil solutions were highly sensitive to acid loading. Simulated acid rain enhanced the leaching of exchangeable base cations out of root zone. Acid inputs resulted in decreased pH, amount of exchangeable base cations and base saturation, in elevated exchangeable acidity and it's Al fraction in soil solid phase. The most significant changes occurred in O and E horizons. Cation exchange, mineral weathering, sulphate adsorption, Al compound transformation and nonexchangeable protonation of soluble and insoluble organic substances were considered as the most significant soil buffering mechanisms.
Computer simulation was used for mathematical analysis of obtained data and model application. The stability of forest soils to acid deposition was assessed using the steady-state mass balance principle implemented as the Simple Mass Balance method for main study areas and the PROFILE model for the permanent monitoring plots. The maps of critical loads and areas where they are exceeded were prepared for forest ecosystems of European Russia. According to calculations critical loads of acidity and sulphur are exceeded in the significant part of the Kola Peninsula (40%). Long-term response to acid deposition of poor sandy podzols under pine and birch forests near the nickel smelter in the Kola Peninsula was evaluated with the dynamic SMART model. The present acid load does not effect considerably on forest soils in background areas. The dramatic shift in soil chemistry near the smelter is expected within several decades. At least 90% of the total SO2 emissions has to be reduced to avoid exceedance of critical values of soil chemical properties and possible serious ecological consequences.
The role of different soil processes was examined on the base of literature reviews and obtained experimental data to get information on soil buffering to acid deposition. The main attention was paid to development of methodology and methods of assessment of soil sustainability to acidifying pollutants and their critical loads for a wide range of forest soil types throughout the different parts of Russia to predict possible negative changes in ecosystems.
Following is a record of publications prepared on the Project topic, listed with the most recent contribution first.
Soil Science Faculty, Moscow State University, Russia | soil.msu.ru/projects/norway/ soil.msu.ru/projects/norway/link/ soil.msu.ru/projects/pollution/ |
Norwegian Forest Research Institute, Norway | www.skogforsk.no |
Norwegian University of Life Sciences | www.nlh.no/ |
International Union of Forestry Research Organisations (IUFRO) | iufro.boku.ac.at |
European Forest Ecosystem Research Network (EFERN) | ifff.boku.ac.at/efern |
International Institute of Applied Systems Analysis, Austria | www.iiasa.ac.at |
National Institute of Public Health and the Environment, the Netherlands | www.rivm.nl/en/ |
Alterra Wageningen University and Research Centre, the Netherlands | www.alterra.wur.nl |
Department of Soil Science, Swedish University of Agricultural Science, Sweden | www.mv.slu.se |
Dept. of Chemical Engineering, University of Lund, Sweden | www2.chemeng.lth.se |
Dr. Galina Koptsik, Soil Science Faculty, Moscow State University
Postal address: | Soil Science Faculty |
Moscow State University | |
Moscow, 119899 | |
Russia | |
Tel.: | +7 495 939 3573 |
Fax: | +7 495 939 0989 |
E-mail addresses: | koptsik@phys.msu.ru |
koptsikg@mail.ru |
Address of this page: http://soil.msu.ru/projects/acidification/