Diatom analysis and the acidification of lakes

Diatom microfossils preserved in lake sediments can be used to provide evidence for lake acidification. Unlike documentary methods of historical reconstruction, the sediment record is potentially useful at all sites, it is usually continuous and it can be extended backwards in time as desired. Cores can be taken with little disturbance, by freezing in situ if necessary, and sediments deposited since about 1800 A.D. can be dated using $^{210}$ Pb analysis. The strong relationship between diatom occurrence and water pH allows pH to be reconstructed with a standard error of between ca. 0.25 and 0.5 pH unit using either an index system or multiple regression analysis. Although there is evidence that long term acidification is a natural process for lakes in areas of resistant base-poor bedrock, diatom analyses from NW European and North American sites shows that rapid acidification has taken place within the last 150 years. The first major sign of acidification is the loss of planktonic diatoms at pH values between about 5.5 and 5.8. Acidification below pH 5.5 leads to the decline of species typical of circumneutral water, such as Achnanthes microcephala Kutz. Cymbella gracilis (Rabh). Cleve and Anomoeoneis vitrea (Grun). Ross, and the expansion of acidophilous taxa such as Tabellaria flocculosa (Roth.) Kutz. and Eunotia veneris (Kutz.) O. Muller. Acidobiontic species become common at pH values less than 5.5 and as the pH drops to 4.5 these taxa begin to replace acidophilous taxa in the assemblage. Tabellaria binalis (Ehr.) Grun. is probably the most faithful member of this group. Diatom analysis for four acid lakes in Galloway, SW Scotland show that the beginning of acidification has varied from 1840 (Loch Enoch) to 1925 (Loch Grannoch) and that pH has declined by between ca. 0.5 units (Loch Dee) and ca. 1.2 pH units (Loch Grannoch) in these lakes. Since lakes without afforested catchments have been acidified and lakes with afforested catchments were acidified before afforestation it can be concluded that afforestation is not responsible for acidification in this region.

[1]  G. H. Evans POLLEN AND DIATOM ANALYSES OF LATE‐QUATERNARY DEPOSITS IN THE BLELHAM BASIN, NORTH LANCASHIRE , 1970 .

[2]  D. Charles Recent pH history of Big Moose Lake (Adirondack Mountains, New York, U. S. A.) inferred from sediment diatom assemblages: With 4 figures in the text , 1984 .

[3]  I.Th. Rosenqvist,et al.  Alternative sources for acidification of river water in norway , 1978 .

[4]  Friedrich Hustedt,et al.  Die Diatomeenflora Des Fluss-Systems Der Weser Im Gebiet Der Hansestadt Bremen , 1976 .

[5]  I. Renberg The pH history of lakes in Southwestern Sweden, as calculated from the subfossil diatom flora of the sediments , 1982 .

[6]  F. Mackereth Some chemical observations on post-glacial lake sediments , 1966, Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences.

[7]  M. Meybeck,et al.  Geochronology of lake sediments , 1971 .

[8]  W. Pearsall,et al.  The development of vegetation in the English lakes, considered in relation to the general evolution of glacial lakes and rock basins , 1921 .

[9]  R. Battarbee CHANGES IN THE DIATOM MICROFLORA OF A EUTROPHIC LAKE SINCE 1900 FROM A COMPARISON OF OLD ALGAL SAMPLES AND THE SEDIMENTARY RECORD , 1981 .

[10]  G. Digerfeldt The Post-Glacial development of Ranviken bay in Lake Immeln. III. Palaeolimnology , 1975 .

[11]  N. Foged On the diatom flora of some Funen lakes , 1954 .

[12]  G. H. Evans,et al.  THE LATE QUATERNARY HISTORY OF THE DIATOM FLORA OF LLYN CLYD AND LLYN GLAS, TWO SMALL OLIGOTROPHIC HIGH MOUNTAIN TARNS IN SNOWDONIA (WALES) , 1977 .

[13]  F. Mackereth A SHORT CORE SAMPLER FOR SUBAQUEOUS DEPOSITS , 1969 .

[14]  Richard J. Beamish,et al.  Acidification of the La Cloche Mountain Lakes, Ontario, and Resulting Fish Mortalities , 1972 .

[15]  R. Battarbee,et al.  Alternative 210Pb dating: results from the New Guinea Highlands and Lough Erne , 1978, Nature.

[16]  T. G. Tutin,et al.  Lake Sediments in Northern Scotland , 1972 .

[17]  Roger J. Flower,et al.  Diatom evidence for recent acidification of two Scottish lochs , 1983, Nature.

[18]  D. Scott,et al.  Acidification and other chemical changes Halifax County lakes after 21 years , 1979 .

[19]  T. G. Tutin,et al.  Observations on Lake Sediments using Fallout 137Cs as a Tracer , 1973, Nature.

[20]  E. Haworth The Diatoms of a Sediment Core from Blea Tarn, Langdale , 1969 .

[21]  N. Quennerstedt Diatoméerna i Långans sjövegetation , 1955 .

[22]  H. Dam,et al.  Man‐made Changes in Some Dutch Moorland Pools, as Reflected by Historical and Recent Data about Diatoms and Macrophytes , 1978 .

[23]  E. G. Jørgensen Diatom communities in some Danish lakes and ponds , 1948 .

[24]  R. Battarbee,et al.  The use of electronically counted microspheres in absolute diatom analysis , 1982 .

[25]  S. Norton,et al.  137Cs and 210Pb dating of sediments from soft-water lakes in New England (U.S.A.) and Scandinavia, a failure of 137Cs dating , 1984 .

[26]  F. E. Round THE LATE‐GLACIAL AND POST‐GLACIAL DIATOM SUCCESSION IN THE KENTMERE VALLEY DEPOSIT , 1957 .

[27]  Richard W. Battarbee,et al.  Diatoms in lake sediments. , 1979 .

[28]  Frank Oldfield,et al.  The calculation of lead-210 dates assuming a constant rate of supply of unsupported 210Pb to the sediment , 1978 .

[29]  F. E. Round THE DIATOMS OF A CORE FROM ESTHWAITE WATER , 1961 .

[30]  I. Renberg,et al.  Dating recent lake sediments by soot particle counting: With 9 figures and 1 table in the text , 1984 .

[31]  N. Foged Freshwater Diatoms in Ireland , 1977 .

[32]  D. Charles,et al.  Mallomonadacean microfossils provide evidence of recent lake acidification , 1984, Nature.

[33]  F. Mackereth,et al.  Chemical investigation of lake sediments and their interpretation , 1965, Proceedings of the Royal Society of London. Series B. Biological Sciences.