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ethanol to 250 g unspiked sediment and stirring the mixture for 1 h. The sediment was<br />

kept at 4 °C until the start of the experiment.<br />

4.3 Test Conditions<br />

The test was evaluated using a 96 h static short-term sediment toxicity<br />

test. There were five replicate test chambers per treatment. Each test chamber<br />

consisted of 600 ml glass beaker with 2-3 cm depth sediment and 400 ml of overlying<br />

water. A hundred of worms per test chamber were used as test organisms. They were<br />

not fed during the exposure period. No aeration was provided for each test chamber.<br />

The water overlying was prepared using deionized water. Test chambers were<br />

covered with a sheet of polyvinylchloride cling film to prevent the evaporation of<br />

naphthalene out off the test medium. All test chambers were conducted at room<br />

temperature with a daily photoperiod of 12 h and kept under the following conditions:<br />

pH, 6.91±0.25; dissolved oxygen, 2.51±0.41 mg/l.<br />

4.4 Exposure Study<br />

1) Range-finding Test<br />

Since there was no reliable data on the toxic level of naphthalene to<br />

L. hoffmeisteri, preliminary test was conducted to find the critical range at first. This<br />

range was defined as an interval between the highest concentration that killed all<br />

worms and the lowest concentration at which all worms survived during the exposure<br />

time (96 h). To determine the critical range, concentration of naphthalene 0.1, 1, 10,<br />

100 and 1,000 µg/g sediment wwt were prepared. The observed result was performed<br />

to determine the concentrations for the definitive test.<br />

2) Definitive Test<br />

Suitable range for the definitive test was determined with five<br />

nominal concentrations (6.25, 12.5, 25, 50 & 100 µg/g sediment wwt as shown in<br />

48

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