Book contents
- Frontmatter
- Contents
- List of contributors
- Preface
- 1 Effects of climate change on fungal diseases of trees
- 2 Effects of climate change on Fusarium foot rot of winter wheat in the United Kingdom
- 3 Effects of UV-B radiation (280–320 nm) on foliar saprotrophs and pathogens
- 4 Implications of global warming and rising sea-levels for macrofungi in UK dune systems
- 5 Red Data Lists and decline in fruiting of macromycetes in relation to pollution and loss of habitat
- 6 Effects of dry-deposited SO2 and sulphite on saprotrophic fungi and decomposition of tree leaf litter
- 7 Effects of atmospheric pollutants on phyllosphere and endophytic fungi
- 8 Influences of acid mist and ozone on the fluorescein diacetate activity of leaf litter
- 9 Mycorrhizas and environmental stress
- 10 Myccorhizas, succession, and the rehabilitation of deforested lands in the humid tropics
- 11 Potential effects on the soil mycoflora of changes in the UK agricultural policy for upland grasslands
- 12 Uptake and immobilization of caesium in UK grassland and forest soils by fungi, following the Chernobyl accident
- 13 Effects of pollutants on aquatic hyphomycetes colonizing leaf material in freshwaters
- 14 Fungi and salt stress
- 15 Fungal sequestration, mobilization and transformation of metals and metalloids
- 16 Urban, industrial and agricultural effects on lichens
- 17 Fungal interactions with metals and radionuclides for environmental bioremediation
- 18 Impact of genetically-modified microorganisms on the terrestrial microbiota including fungi
- 19 Has chaos theory a place in environmental mycology?
- Index of generic and specific names
- Subject index
6 - Effects of dry-deposited SO2 and sulphite on saprotrophic fungi and decomposition of tree leaf litter
Published online by Cambridge University Press: 05 November 2011
- Frontmatter
- Contents
- List of contributors
- Preface
- 1 Effects of climate change on fungal diseases of trees
- 2 Effects of climate change on Fusarium foot rot of winter wheat in the United Kingdom
- 3 Effects of UV-B radiation (280–320 nm) on foliar saprotrophs and pathogens
- 4 Implications of global warming and rising sea-levels for macrofungi in UK dune systems
- 5 Red Data Lists and decline in fruiting of macromycetes in relation to pollution and loss of habitat
- 6 Effects of dry-deposited SO2 and sulphite on saprotrophic fungi and decomposition of tree leaf litter
- 7 Effects of atmospheric pollutants on phyllosphere and endophytic fungi
- 8 Influences of acid mist and ozone on the fluorescein diacetate activity of leaf litter
- 9 Mycorrhizas and environmental stress
- 10 Myccorhizas, succession, and the rehabilitation of deforested lands in the humid tropics
- 11 Potential effects on the soil mycoflora of changes in the UK agricultural policy for upland grasslands
- 12 Uptake and immobilization of caesium in UK grassland and forest soils by fungi, following the Chernobyl accident
- 13 Effects of pollutants on aquatic hyphomycetes colonizing leaf material in freshwaters
- 14 Fungi and salt stress
- 15 Fungal sequestration, mobilization and transformation of metals and metalloids
- 16 Urban, industrial and agricultural effects on lichens
- 17 Fungal interactions with metals and radionuclides for environmental bioremediation
- 18 Impact of genetically-modified microorganisms on the terrestrial microbiota including fungi
- 19 Has chaos theory a place in environmental mycology?
- Index of generic and specific names
- Subject index
Summary
Sulphur pollution – past trends, current levels
Sulphur (S) is an essential element for the growth and activity of organisms, occuring free in abundant quantities. It is found in valence states ranging from +6 in sulphates to -2 in sulphides, the most stable state being S6+. Globally, natural emissions of S into the atmosphere from biogenic sources have been estimated to range between 78.9 and 142.6 Tg yr-1, of which 5.0 to 63.9 Tg yr-1 arises from land (Schlesinger, 1991; Andreae & Jaeschke, 1992; Germida, Wainwright & Gupta, 1992). Estimates of the relative significance of anthropogenic to natural sulphur emissions are variable, but globally the ratio is probably about 4: 1 (Möller, 1984), atmospheric S emissions from land being in the order: anthropogenic 93 Tg yr-1 > biogenic gases 22 > dust 20 > volcanoes 10 (Brimblecombe et al., 1989). Sulphur emissions to the atmosphere are not constant with time, having increased dramatically since the industrial revolution as a result of combustion of fossil fuels. Global anthropogenic emissions have increased from an estimated 5 Tg in 1860 to 180 Tg in 1985, with considerable increases predicted up to 2000 (Fig. 6.1; Möller, 1984; Schlesinger, 1991), despite electives by European countries to have reduced emissions by 1993 to 30% of 1980 emissions.
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- Fungi and Environmental Change , pp. 70 - 89Publisher: Cambridge University PressPrint publication year: 1996
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