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Maberly Maberly (1992)
Carbonate ions appear to neither inhibit nor stimulate use of bicarbonate ions in photosynthesis byUlva lactuca. Plant Cell & Environment, 15
S. Emerson (1975)
Gas exchange rates in small Canadian Shield lakes1Limnology and Oceanography, 20
H. Harned, Raymond Davis (1943)
The Ionization Constant of Carbonic Acid in Water and the Solubility of Carbon Dioxide in Water and Aqueous Salt Solutions from 0 to 50Journal of the American Chemical Society, 65
S. Heaney, W. Smyly, J. Talling (1986)
Interactions of physical chemical and biological processes in depth and time within a productive English lake during summer stratificationInternational Review of Hydrobiology, 71
Harned Harned, Davis Davis (1943)
The ionization constant of carbonic acid in waterJournal of the American Chemical Society, 65
W. House (1987)
Inhibition of calcite crystal growth by inorganic phosphateJournal of Colloid and Interface Science, 119
J. Truchot, A. Duhamel-Jouve (1980)
Oxygen and carbon dioxide in the marine intertidal environment: diurnal and tidal changes in rockpools.Respiration physiology, 39 3
R. Jacobson, D. Langmuir (1974)
Dissociation constants of calcite and CaHC03+ from 0 to 50°CGeochimica et Cosmochimica Acta, 38
P. Liss, L. Merlivat (1986)
Air-Sea Gas Exchange Rates: Introduction and Synthesis
U. Riebesell, U. Riebesell, D. Wolf-Gladrow, V. Smetácek (1993)
Carbon dioxide limitation of marine phytoplankton growth ratesNature, 361
R. Upstill‐Goddard, A. Watson, P. Liss, M. Liddicoat (1990)
Gas transfer velocities in lakes measured with SF6Tellus B, 42
J. Cole, N. Caraco, G. Kling, T. Kratz (1994)
Carbon Dioxide Supersaturation in the Surface Waters of LakesScience, 265
G. Kling, G. Kipphut, Michael Miller (1991)
Arctic Lakes and Streams as Gas Conduits to the Atmosphere: Implications for Tundra Carbon BudgetsScience, 251
S. Maberly (1985)
Photosynthesis by Fontinalis antipyretica. II: Assessment of environmental factors limiting photosynthesis and productionNew Phytologist, 100
J. Talling (1971)
The underwater light climate as a controlling factor in the production ecology of freshwater phytoplankton: With 14 figures in the text and on 1 folder, 19
J. Howard, G. Skirrow, W. House (1984)
Major ion and carbonate system chemistry of a navigable freshwater canalFreshwater Biology, 14
J. Darbyshire, A. Edwards (1972)
Seasonal formation and movement of the thermocline in lakespure and applied geophysics, 93
P. Quay, S. Emerson, B. Quay, A. Devol (1986)
The carbon cycle for Lake Washington—A stable isotope study1Limnology and Oceanography, 31
S. Maberly, D. Spence (1983)
PHOTOSYNTHETIC INORGANIC CARBON USE BY FRESHWATER PLANTSJournal of Ecology, 71
E. Sholkovitz, D. Copland (1982)
The chemistry of suspended matter in Esthwaite Water, a biologically productive lake with seasonally anoxic hypolimnionGeochimica et Cosmochimica Acta, 46
W. House, J. Howard, G. Skirrow (1984)
Kinetics of carbon dioxide transfer across the air/water interfaceFaraday Discussions of The Chemical Society, 77
Norton Norton, Henriksen Henriksen (1983)
The importance of CO2 in evaluation of effects of acidic depositionVatten, 39
E. Tipping, J. Hilton, B. James (1988)
Dissolved organic matter in Cumbrian lakes and streamsFreshwater Biology, 19
W. Deuser (1970)
Isotopic Evidence for Diminishing Supply of Available Carbon during Diatom Bloom in the Black SeaNature, 225
A. Akgerman, J. Gainer (1972)
Predicting gas-liquid diffusivitiesJournal of Chemical & Engineering Data, 17
G. Kling, G. Kipphut, Michael Miller (1992)
The flux of CO2 and CH4 from lakes and rivers in arctic AlaskaHydrobiologia, 240
A. Herczeg, R. Hesslein (1984)
Determination of hydrogen ion concentration in softwater lakes using carbon dioxide equilibriaGeochimica et Cosmochimica Acta, 48
J. Etcheto, L. Merlivat (1989)
Global determinations of the carbon dioxide exchange coefficient-comparison of wind speed from different originsAdvances in Space Research, 9
S. Maberly (1992)
Carbonate ions appear to neither inhibit nor stimulate use of bicarbonate ions in photosynthesis by Ulva lactucaPlant Cell and Environment, 15
J. Talling (1976)
The depletion of carbon dioxide from lake water by phytoplanktonJournal of Ecology, 64
W. Davison, M. Hill, C. Woof, M. Rouen, D. Aspinall (1994)
Continuous measurement of stream pH. Evaluation of procedures and comparison of resulting hydrogen ion budgets with those from flow-weighted integrating samplersWater Research, 28
W. Davison (1990)
A practical guide to pH measurement in freshwatersTrends in Analytical Chemistry, 9
Yuan-hui Li, S. Gregory (1974)
Diffusion of ions in sea water and in deep-sea sedimentsGeochimica et Cosmochimica Acta, 38
Talling Talling (1971)
The underwater light climate as a controlling factor in the production ecology of freshwater phytoplanktonMitteilungen der Internationale Vereinigung für Theoretische und Angewandte Limnologie, 19
W. Davison, S. Heaney, J. Talling, E. Rigg (1980)
Seasonal transformations and movements of iron in a productive English lake with deep-water anoxiaSchweizerische Zeitschrift für Hydrologie, 42
P. Quay, W. Broecker, R. Hesslein, D. Schindler (1980)
Vertical diffusion rates determined by tritium tracer experiments in the thermocline and hypolimnion of two lakes1,2Limnology and Oceanography, 25
D. Sutcliffe, T. Carrick (1988)
Alkalinity and pH of tarns and streams in the English Lake District (Cumbria)Freshwater Biology, 19
U. Siegenthaler (1986)
Carbon Dioxide: Its Natural Cycle and Anthropogenic Perturbation
W. House (1990)
The prediction of phosphate coprecipitation with calcite in freshwatersWater Research, 24
A. Watson, Carol Robinson, J. Robinson, PJ Williams, M.J.R. Fasham (1991)
Spatial variability in the sink for atmospheric carbon dioxide in the North AtlanticNature, 350
D. Schindler, E. Fee (1973)
Diurnal Variation of Dissolved Inorganic Carbon and its Use in Estimating Primary Production and CO2 Invasion in Lake 227Wsq: Women's Studies Quarterly, 30
J. Talling (1973)
The application of some electrochemical methods to the measurement of photosynthesis and respiration in fresh watersFreshwater Biology, 3
W. Pearsall (1921)
The development of vegetation in the English lakes, considered in relation to the general evolution of glacial lakes and rock basinsProceedings of The Royal Society B: Biological Sciences, 92
A. Rebsdorf, N. Thyssen, M. Erlandsen (1991)
Regional and temporal variation in pH, alkalinity and carbon dioxide in Danish streams, related to soil type and land useFreshwater Biology, 25
G. Kell (1967)
Precise representation of volume properties of water at one atmosphereJournal of Chemical & Engineering Data, 12
Heaney Heaney, Smyly Smyly, Talling Talling (1986)
Interactions of physical, chemical and biological processes in depth and time within a productive English lake during summer stratificationInternationale Revue der Gesamten Hydrobiologie, 71
Rudd Rudd, Harris Harris, Kelly Kelly, Hecky Hecky (1993)
Are hydroelectric reservoirs significant sources of greenhouse gasesAmbio, 22
J. Talling (1993)
Comparative seasonal changes, and inter-annual variability and stability, in a 26-year record of total phytoplankton biomass in four English lake basinsHydrobiologia, 268
D. George, D. Hewitt, J. Lund, W. Smyly (1990)
The relative effects of enrichment and climate change on the long-term dynamics of Daphnia in Esthwaite Water, CumbriaFreshwater Biology, 23
SUMMARY 1 Two pH electrodes and a thermistor were used to record conditions in the surface of Esthwaite Water every 15 min over a 12‐month period. Combined with approximately weekly measurements of alkalinity they allowed inorganic carbon speciation to be calculated. 2 Large changes in pH from 7.1 to nearly 10.3, and hence in concentrations of inorganic carbon species, were measured over a year. Carbon speciation and pH varied on a diel, episodic and seasonal basis. Diel variation of up to pH 1.8 was recorded, although typical daily variation was between 0.03 and 1.06 (5 and 95 percentiles). Daily change in concentration of inorganic carbon varied between 4 and 63 mmol m‐3 (5 and 95 percentiles). 3 During lake stratification, episodes of high pH, typically of 1–2 weeks' duration were interspersed with episodes of lower pH. These changes appeared to relate to the weather: e.g. low wind velocity, high pressure, low rainfall and high sunshine hours correlated with periods of high pH. 4 Seasonal progression of carbon depletion generally followed stratification and the development of high phytoplankton biomass. When the lake was isothermal, the phytoplankton biomass caused relatively small amounts of carbon depletion. 5 During autumn, winter and spring, the lake had concentrations of CO2* (free CO2) up to 0.12 mol m‐3 which is nearly seven times the calculated atmospheric equilibrium concentration so the lake will accordingly be losing carbon to the atmosphere. In contrast, during periods of elevated pH the concentration of CO2* was reduced close to zero and the lake will take up atmospheric CO2. The rates of transfer between water and the atmosphere were estimated using a chemical equilibrium model with three boundary layer thicknesses. The calculations show that over a year the lake loses CO2 to the atmosphere with the current mean atmospheric level of 360 μmol mol‐1, at between 0.28 and 2.80 mol m‐2 yr‐1. During elevated pH, rates of CO2‐influx increased up to nearly tenfold as a result of chemical‐enhancement by parallel flux of HCO‐3. Input of CO2* to the lake from the catchment is suggested to be the main source of the carbon lost to the atmosphere. 6 The turnover time for CO2 between the air and water was calculated to be 1 year for the gross influx and 3.3 years for the net flux. These values are less than the average water residence time of 0.25 years, which indicates that over a year inflow from streams is a more important source of inorganic carbon than the atmosphere. 7 Influx of CO2 from the atmosphere was calculated to be roughly equivalent to between 1 and 4% of the rates of production in the water during mid‐summer indicating that this source of inorganic carbon is not a major one in this lake. 8 Influx of CO2 from the hypolimnion was estimated on one occasion to be 6.9 10‐9 mol m‐2 s‐1 using transfer values based on mass eddy‐diffusion. These rates are equivalent to 23% of the rate of influx of CO2 from the atmosphere on this occasion which suggests that the hypolimnion is probably a small source of inorganic carbon to the epilimnion. The exception appears to be during windy episodes when pH is depressed. Calculations based on depth‐profiles of CO2* and HCO‐3 suggest that the measured changes in pH can be accounted for by entrainment of hypolimnetic water into the epilimnion. 9 The solubility product for calcite was exceeded by up to about sixfold which, although insufficient to allow homogeneous precipitation, may have allowed heterogeneous precipitation around algal particles.
Freshwater Biology – Wiley
Published: Jun 1, 1996
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