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Activity pattern and food habits of Grizzled Giant Squirrel were investigated in Srivilliputhur Grizzled Giant Squirrel Wildlife Sanctuary from December 2011 to March 2012. Focal animal sampling method was used to record the activity pattern and food habits. Sampling was done in three different habitats viz., Private land, Reserve forest and Temple land. Feeding was the dominant activity accounting for 35.4% of the activity period. Bimodal feeding pattern was observed in Squirrels, the observations were made from early morning hours to till (0600-1800) late evening hours. The Squirrels feed upon 23 plant species; among them 11 were trees species, 10 climbers and 2 shrubs. Seven types of plant parts were used by Squirrels. Leaf consumption was high (38%) followed by fruit (24%). The high consumption of leaves was due to easy availability of leaves and limited availability of other plant parts. Squirrel‟s invasion into Private Land and Temple Land was observed which can be attributed to abundance and easy availability of food plants, canopy continuity and less predatory pressure.
Background. Copper is a heavy metal, and an aquatic pollutant, known for its bio-accumulative and non-biodegradable properties. In the aquatic ecosystems, acute and sublethal concentrations of copper may be linked to a variety of effects. Recently, hormones, particularly those regulating vital functions, such as osmoregulation, energy metabolism, and reproduction, may be used as potential biomarkers for sublethal toxicity studies. In the present study, the potential effect of a heavy metal—copper on hormonal changes (cortisol and prolactin) in an economically important fresh-water fish—common carp, Cyprinus carpio, was examined. Materials and Methods. The experimental fish were subjected to two experimental regimes (backed by controls). In the first treatment they were exposed to the acute concentration of copper sulphate, amounting to 0.7 ppm. The second treatment featured copper sulphate concentration of 0.07 ppm, constituting 10% of LC50 (24 h). The acute-toxicity trials were carried out in two, 20-L, circular plastic tubs. Twenty fish from the tank were selected randomly and introduced to each tub. Control was maintained in 2 similar plastic tubs with 20 fish per tub. After 24 h, fish from control- and copper-exposure tubs were taken for analyses. To observe the sublethal toxicity four, 125-L, glass aquaria, filled with clean water were used. 200 fish were randomly selected from the stock and 100 of them were added to two aquaria, 50 fish in each, as experimental fish and 100 in two other aquaria, 50 in each, for as control fish. By the end of the stipulated period, 20 fish from control and 20 fish from experimental group were used for the hormone assay. Results. In both acute- and sublethal treatments, both cortisol- and prolactin levels increased. In sublethal treatment, however, plasma prolactin level decreased after 28-day exposure, showing a minimum percentage point decrease of 3.84 by the end of 35-day trial. Conclusion. The increase of the plasma cortisol was probably caused by release of cortisol from the interrenal tissue, as a mechanism of coping with stress. Significantly lower content of prolactin levels in sublethal treatment could be an indicative of a possible restored hydromineral balance or atrophy of the pituitary prolactin cells leading to inhibited prolactin secretion of the fish. These alterations of the above hormonal changes may be used as stress biomarkers in fish.
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