Recovery from acidification in central Europe: observed and predicted changes of soil and streamwater chemistry in the Lysina catchment, Czech Republic

• Published in: Environmental pollution (1987) 2002-01, Vol.120 (2), p.261-274
• Main Authors: HRUSKA, Jakub, MOLDAN, Filip, KRAM, Pavel
• Format: Article
• Language: English
• Subjects: Acid Rain; Applied sciences; Biodegradation, Environmental; Biological and physicochemical properties of pollutants. Interaction in the soil; Computer Simulation; Continental surface waters; Czech Republic; Earth sciences; Earth, ocean, space; Engineering and environment geology. Geothermics; Environmental Health; Environmental Pollution - analysis; Exact sciences and technology; Forestry; Fresh Water - analysis; Geologic Sediments; Hydrogen-Ion Concentration; Models, Theoretical; Natural water pollution; Pollution; Pollution, environment geology; Soil and sediments pollution; Time Factors; Trees; Water treatment and pollution
• ISSN: 0269-7491; 1873-6424
• DOI: 10.1016/S0269-7491(02)00149-5

The geochemical model MAGIC was applied to estimate streamwater and soil chemistry between 1851 and 2030 at the Lysina catchment, an acid-sensitive granitic catchment covered by planted Norway spruce monoculture in the western Czech Republic. The total deposition of sulfur to the catchment was 164 meq m(-2) in 1991, but had declined to 52 meq m(-2) by 2000. Although SO2 emissions in the region declined by 90% compared to the 1980s, acidification recovery was small within the period 1990-2000. Stream pH increased only slightly (from 3.92 to 4.07), although SO4 concentration declined sharply from 568 microeq l(-1) (1990) to 232 microeq l(-1) (2000). Organic acids played an important role in streamwater buffering. According to the MAGIC prediction using deposition measured in 1999-2000, streamwater pH will increase to 4.3 and soil base saturation will increase to 6.2% by 2030 (from 5.7% in 2002). Pre-industrial pH was estimated to be 5.5 and soil base saturation 24.7%. The loss of base cations (Ca, Mg, Na, K) was caused predominantly by atmospheric acidity, but intensive forestry was responsible for approximately one third of the net base cation loss via accumulation in harvested biomass. Severely damaged sites, under continued pressure from forestry, will not return to a good environmental status in the near future (if ever) when the acid deposition input is only partially reduced.