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Flameless: 0.000 I mgll (solution)<br />

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 />

isobutyl ketone (MlBK).<br />

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

C. Extraction<br />

(I) Place 100 ml of solution in a 250-ml acid-washed separatory funnel. Add 2 ml of chelating<br />

reagent and add 5 ml ofMIBK.<br />

(2) Shake thorough Iy for about 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 />

6.7 Lead (Atomic Absorption)<br />

I. Concentrations<br />

Average river water 1-10 fLg11<br />

Average nearshore sediment 20 mg/kg<br />

Sea water"" 0.02 - 0.1 fLg11<br />

The dissolved sediment as prepared in Section 6.2 is analyzed by flame atomic absorption with the<br />

following operating parameters:<br />

A. Detection Limits<br />

Flame: 0.05 mgll (solution) ( = 50 mg/kg in sediment)<br />

B. Working Range<br />

Linear response can be expected from the spectrometer up to 20 mgll (solution) (=20 mg/ kg in<br />

sediment).<br />

C. Interferences<br />

No serious chemical interferences. Background corrector is highly advantageous.<br />

D. Instrument Parameters<br />

Wavelength: 283.3 nm<br />

Fuel: air I acetylene<br />

Check manufacturer's handbook<br />

Flame: oxidizing (lean. blue)<br />

II. Solvent Extraction<br />

This method is necessary for the low concentrations found in seawater.<br />

A. Detection Limits<br />

Flameless: 0.00002 mgll(solution)<br />

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