The effect of reduced atmospheric deposition on soil and soil solution chemistry at a site subjected to long-term acidification, Nacetín, Czech Republic
Language English Country Netherlands Media print-electronic
Document type Journal Article, Research Support, Non-U.S. Gov't
PubMed
16935320
DOI
10.1016/j.scitotenv.2006.07.031
PII: S0048-9697(06)00572-9
Knihovny.cz E-resources
- MeSH
- Chemical Precipitation MeSH
- Chlorides analysis MeSH
- Nitrates analysis MeSH
- Hydrogen-Ion Concentration MeSH
- Metals analysis MeSH
- Quaternary Ammonium Compounds analysis MeSH
- Acid Rain * MeSH
- Soil Pollutants analysis MeSH
- Air Pollutants analysis MeSH
- Environmental Monitoring MeSH
- Soil analysis MeSH
- Sulfur analysis MeSH
- Sulfates analysis MeSH
- Picea chemistry MeSH
- Publication type
- Journal Article MeSH
- Research Support, Non-U.S. Gov't MeSH
- Geographicals
- Czech Republic MeSH
- Names of Substances
- Chlorides MeSH
- Nitrates MeSH
- Metals MeSH
- Quaternary Ammonium Compounds MeSH
- Acid Rain * MeSH
- Soil Pollutants MeSH
- Air Pollutants MeSH
- Soil MeSH
- Sulfur MeSH
- Sulfates MeSH
During the 1990s the emissions of SO(2) fell dramatically by about 90% in the Czech Republic; the measured throughfall deposition of sulphur to a spruce forest at Nacetín in the Ore Mts. decreased from almost 50 kg ha(-1) in 1994 to 15 kg ha(-1) in 2005. The throughfall flux of Ca decreased from 17 kg ha(-1) in 1994 to 9 kg ha(-1) in 2005; no change was observed for Mg. The deposition of nitrogen ranged between 15 and 30 kg ha(-1) with no statistically significant trend in the period 1994-2005. The desorption of previously stored sulphur and the decrease of Ca deposition are the main factors controlling the recovery of soil solution. The pH of the soil solution at a depth of 30 cm remains unchanged, and the Al concentration decreased from 320 micromol l(-1) in 1997 to 140 micromol l(-1) in 2005. The enhanced leaching of base cations relative to no acidified conditions has continued, although the Ca concentration decreased from 110 microeq l(-1) in 1997 to 25 microeq l(-1) in 2005 in the mineral soil solution at 30 cm depth. This dramatic change was not observed for Mg concentration in soil solution, because its deposition remained stable during the observed period. Similar patterns were observed in the deeper soil solution at 90 cm. The reduction in Ca availability resulted in lower uptake by tree assimilatory tissues, measured as concentration in needles. Since 2005, the leaching of nitrate observed in soil solution at 30 cm depth has disappeared. By 2003 a similar situation occurred at 90 cm. Higher incorporation into the trees after 1997 could be an important factor. With respect to the formerly high sulphur deposition and consequently released aluminium, which could have negatively influenced the biotic immobilization driven by microbes and fungi, the recovery may have positively impacted and therefore improved retention in the ecosystem during recent years. The delay in the successful retention of nitrogen in the ecosystem was probably caused by the high mineralization of organic matter after improvement of chemical parameters in the organic horizon (increase in pH and decrease in Al concentration). It seems that high mineralization of stored organic matter after decades of high acidic deposition could be an important factor affecting the high losses of nitrogen in spruce forest ecosystems.
References provided by Crossref.org
Forest growth responds more to air pollution than soil acidification
Mobility of Pb, Zn, Cu and As in disturbed forest soils affected by acid rain
Release of mobile forms of hazardous elements from glassworks fly ash into soils