During a four-year study of food chains in Loch Ewe on the west of Scotland, the bivalve Tellina tenuis da Costa has been studied in some detail. Data have been collected for two populations in Loch Ewe, one in Firemore Bay, which has been studied in more detail, and one in Inverasdale. For comparison another population outside Loch Ewe, in nearby Gruinard Bay, has also been sampled. Tellina tenuis occurs from mid-tide level down to a few metres below low water. It lies in the sand at a depth of a few centimetres, generally on its left side. The inhalant siphon extends more or less vertically into the water column while faeces and water are expelled through the exhalant siphon which is usually extended into the sand more or less horizontally below the surface. Food, consisting of plankton and organic detritus, is probably obtained mainly from the sand-water interface, and the siphons do not normally extend far above the surface. Experimentally, low oxygen content, extremes of temperature, and lack of food may stimulate the inhalant siphons to extend further out into the water. At low tide it is thought that Tellina takes in interstitial water, and with it some sand grains. Filtration rates, measured as the clearance of a Phaeodactylum suspension were 20–60 ml/h for animals of 15–20 mg dry weight, giving ingestion of at least 250 μg of particulate organic matter per day if active filtration occurs during 50 % of the time. Oxygen uptake was measured over the natural temperature range throughout the year and a value of 6 mg O 2/g/day has been suggested as a mean value for the year. The inhalant siphons are preyed upon by 0-group plaice. The extent of predation varied during the years studied. Changes are partly due to changes in the relative density of predator and prey, and also in the abundance of other prey species such as polychaetes. Siphon regeneration occurs at the rate of about 0.3 mg/week. The ‘condition’ (dry flesh weight of a standard animal) of Tellina from the three beaches shows a similar seasonal pattern with low values in the winter, a rise in the spring, one or two peaks in the summer and a fall in the autumn to the low winter values. The peaks are largely due to gonad proliferation, with a sudden decrease on spawning, The ‘condition’ of Tellina at the three localities has improved from 1967 to 1968, and in Firemore has improved steadily since 1965. Relevant climatic data have been examined. The seasonal pattern of growth follows closely the changes in temperature, which may have a direct effect on growth and an indirect effect via the food supply. Northerly winds may have an adverse effect on the condition of Tellina in Loch Ewe since they give rise to a swell and so to sand disturbance, which in turn may prevent the animals from feeding normally. In 1968 there was more bright sunshine and less rain than in the three previous years and this may partly explain the good growth and condition of Tellina in that year. Similarly, high rainfall and low values for hours of sunshine may have had an adverse effect on Tellina in 1967. Heavy mortalities and very small recruitment to the population of Tellina in Firemore Bay have resulted in a decrease in population numbers. A table of production data has been drawn up to show the proportion of energy channelled into growth, reproduction, siphon regeneration, and respiration. Factors which may affect the changes in production of the Tellina population in Firemore Bay are discussed, and the growth efficiency is compared with published data for some other invertebrates.
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