121 |
The historical and evolutionary development of the plant life of St. HelenaCronk, Q. C. B. January 1984 (has links)
No description available.
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122 |
The control of helminths in farm and sewage effluentsHolah, J. T. January 1986 (has links)
No description available.
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123 |
Ecological studies of insect reproductive behaviourMayhew, Peter J. January 1996 (has links)
No description available.
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124 |
Studies on the effect of population size and selection intensity on artificial selectionOsorio, Mario M. January 1981 (has links)
No description available.
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125 |
The ecology and behaviour of Chital (Axis axis) in the Royal Chitwan National Park, Nepal : with comparative studies of hog deer (Axis porcinus), sambar (Cervus unicolor) and Barking deer (Muntiacus muntjak)Mishra, Hemanta Raj January 1982 (has links)
No description available.
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126 |
Social organisation and feeding behaviour of wintering turnstone (Arenaria interpres)Whitfield, Douglas Philip January 1985 (has links)
No description available.
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127 |
The life history and ecology of the common cleg, Haematopota pluvialis, in the West of ScotlandThomson, Robert Campbell Kennedy January 1986 (has links)
No description available.
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128 |
A comparison of the ecology of fallow deer (Dama dama L.), cattle and sheep on a shared rangelandChaudhary, Abdul Aleem January 1985 (has links)
No description available.
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129 |
Aspects of the plant ecology of a flood-plain mire in broadland, NorfolkGiller, Kenneth E. January 1982 (has links)
Vegetation of a particularly diverse area of undrained flood-plain mire is described. Factors and processes important in determining the distribution of community-types within the study area have been investigated. Investigation of the alluvial stratigraphy has revealed the presence of a complex pattern of peat cuttings. Succession within the peat cuttings, with appropriate vegetation management, has led to the formation of Cladium mariscus-, Phragmites communis- and Juncus subnodulosus-dominated fen vegetation and, in some areas, poor-fen communities with much Sphagnum. In areas not cut for peat, management his also sustained various rich-fen herbaceous communities(different to those of the cuttings); in its absence, fen carr develops. The differences in successional development in peat cutting areas and those not cut for peat is mainly due to difference in hydrological status. Long term experiments established to examine effects of different management techniques are described. Studies of peat and peat water chemistry in a representative selection of community-types has demonstrated local areas of high salinity, caused by incursions of brackish water due to exceptionally high tides and, particularly, the influence of underlying estuarine deposits. Although large areas are flooded by river water there is little evidence for eutrophication, except very locally. Indeed, 'seral oligotrophication' is occurring in isolated areas. This may preceed, but is not a pre-requisite for, Sphagnum invasion. The most species-rich communities are developed in non-saline areas with a fairly stable water level; they may, however, be dependent upon flooding by river water for maintenance of their base status.
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130 |
The ecology of Dunlin (Calidris alpina L.) wintering on the Severn EstuaryClark, Nigel Anthony January 1983 (has links)
No description available.
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