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1 - Cochin University of Science and Technology

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measurement <strong>of</strong> temperature, salinity, pH, dissolved oxygen <strong>and</strong> nutrients.<br />

Temperature <strong>of</strong> water was measured in the field itself. For estimation <strong>of</strong><br />

dissolved oxygen, water was taken in 125 ml stoppered glass bottles taking<br />

care that no air bubbles were trapped in the sample <strong>and</strong> fixed with Winkler<br />

solutions. For salinity, pH <strong>and</strong> nutrients estimation, water samples were<br />

collected in plastic bottles <strong>and</strong> taken to the laboratory <strong>and</strong> stored in an<br />

insulated box till they were analysed. Interstitial water was taken with the<br />

help <strong>of</strong> an air stone, connected to a plastic siphoning tube <strong>and</strong> a pipette<br />

connected to the other end <strong>of</strong> the tube, by h<strong>and</strong> vacuum suction method<br />

(Sarda <strong>and</strong> Burton, 1995). The stone was inserted in the sediment to the<br />

desired depth <strong>and</strong> then only suction applied.<br />

2. 4. 2. Sediment: Sediments for grain size analysis <strong>and</strong> organic carbon<br />

estimation were taken at low tide from each station. Samples were taken<br />

with a plexiglass corer <strong>of</strong> 5 cm diameter up to a depth <strong>of</strong> 10 cm (Holme<br />

<strong>and</strong> Mc Intyre, 1984). Samples were tied in polythene bags <strong>and</strong> taken to<br />

the laboratory for analysis.<br />

2. 4. 3. Benthos: Triplicate samples were collected every month using a<br />

metal quadrat <strong>of</strong> 25cm X 25cm size up to a depth <strong>of</strong> 15 cm (Ansari et aI.,<br />

1984; Eleftheriou <strong>and</strong> Holme, 1984). Quadrat data was gathered at 10 m<br />

intervals along 10 m distant transect lines (drawn perpendicular to the main<br />

parallel shore line), which were selected by r<strong>and</strong>om sampling every month.<br />

This method followed recommendations by Hiscock (1987), Hiscock <strong>and</strong><br />

Mitchell (1989) <strong>and</strong> Bakus (1990). All samples were collected during low<br />

tide when maximum intertidal exposure prevailed <strong>and</strong> were sieved by a 0.5<br />

mm metal sieve (Birkett <strong>and</strong> Mc Intyre, 1971; Holme <strong>and</strong> Mc Intyre, 1984)<br />

in the nearby running water <strong>and</strong> the residue retained on the sieve was<br />

collected in polythene bag <strong>and</strong> carried to the laboratory for further analysis.<br />

16

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