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B. Reagents<br />

Chelating reagent: ammonium pyrrolidinedithiocarbamate (APDC) or sodium diethyldithiocarbamate<br />

(DEDC). Make up a 5% solution with deionized-distilled water. Extract at least twice with methyl<br />

isobu tyl ketone (MIBK).<br />

Methyl isobutyl ketone (MIBK) (distilled).<br />

C. Extraction<br />

(I) Place 50 ml of solution in a 250-ml acid-washed separatory funnel. Add 2 ml ofchelating reagent<br />

and add 5 ml of MIBK.<br />

(2) Shake thoroughly for abou t 3 min and save the upper (extract) layer for analysis.<br />

D. Analysis<br />

For flame conditions, adjust the spectrometer settings as above. It may be necessary if the metal<br />

concentrations are very low to use the flameless attachment of the atomic absorption spectrometer. Check<br />

manufacturer's handbook.<br />

Note: Where greater sensitivity is required the flameless method can be employed. In all methods, however,<br />

it is well known that difficulties can arise through contamination from reagents, samplers, and<br />

containers.<br />

6.11 Extra Notes on Metal Analysis<br />

I. Quantity of MIBK<br />

The quantity of MIBK extraction solvent determines the concentration factor. It should be noted that<br />

no extraction is 100% efficient and the solubility of MIBK in water is 2%.<br />

II. Contamination<br />

( I) The purity of the MIBK is im proved by distillation.<br />

(2) Only high purity acids should be used when the sample is acidified for storage.<br />

(3) Any chelating reagent should be extracted twice before use.<br />

(4) Care should be taken that all glassware is thoroughly washed in conc. nitric acid and deionizeddistilled<br />

water.<br />

III. Atomic Fluorescence Spectroscopy<br />

A number of authors have suggested measuring metal concentrations by atomic fluorescence rather<br />

than atomic absorption because this method has lower detection limits. However, most laboratories do not<br />

have the necessary instrumentation or expertise.<br />

IV. Anodic Stripping Voltametry<br />

This technique is still under development and has not received the degree of acceptance accorded to<br />

atomic absorption approaches.<br />

6.12 Mercury (Cold Vapour Atomic Absorption Technique)<br />

I. Concentrations<br />

Average river water"" 0.08 j.tgl I<br />

Nearshore sediments"" 390 j.tg/kg (Loring 1975)<br />

Coastal seawater 0.058-0.071 j.tgl I (Cranston and Buckley 1972)<br />

39

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