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Resonance light scattering method for the determination of anionic ...

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X. Xiao et al. / Spectrochimica Acta Part A 71 (2008) 398–402 401<br />

Table 1<br />

Analytical parameters<br />

Method<br />

Concentration <strong>of</strong> AO<br />

(×10 −5 mol L −1 )<br />

Linear range<br />

(mg L −1 )<br />

Linear regression<br />

equation ρ (mg L −1 )<br />

Correlation<br />

coefficient r<br />

Limit <strong>of</strong> <strong>determination</strong><br />

(3δ) ((g L −1 )<br />

RRS 2.50 0.028–8.71 I = −18.1 + 31.2ρ 0.992 8.36<br />

FDS 2.50 0.014–8.71 I = 0.02 + 6.1ρ 0.993 4.31<br />

SOS 2.50 0.050–8.71 I = 0.19 + 4.3ρ 0.993 14.9<br />

Table 2<br />

Determination results <strong>of</strong> water samples (n =6)<br />

Sample<br />

Found<br />

(mg L −1 )<br />

R.S.D.<br />

S r (%)<br />

SDBS<br />

added (g)<br />

Recovery <strong>of</strong><br />

SDBS (g)<br />

Recovery<br />

R (%)<br />

Methylene-blue<br />

<strong>method</strong> ρ (mg L −1 )<br />

t<br />

Running water 0.057 4.0 1.74 1.64 94.3 0.059 1.01<br />

Xiangjiang river water 0.079 3.0 1.74 1.68 96.6 0.082 2.12<br />

Pond water 0.109 1.8 1.74 1.81 104.0 0.112 1.69<br />

3.3.3. Influence <strong>of</strong> reaction temperature, standing time and<br />

adding sequence<br />

We tested <strong>the</strong> influence <strong>of</strong> temperature on <strong>the</strong> intensity <strong>of</strong><br />

resonance <strong>light</strong> <strong>scattering</strong> <strong>of</strong> this reactive system. 15 ◦ C was <strong>the</strong><br />

optimal reaction temperature. The reaction could be generated<br />

instantly and <strong>the</strong> standing time should last 2 h. This experiment<br />

preferred 10 min as <strong>the</strong> determining time.<br />

Three adding sequences <strong>of</strong> reagents were tested in this experiment:<br />

first, mix AO and SDBS and <strong>the</strong>n added <strong>the</strong> buffer<br />

solution; second, added AO into buffer solution and <strong>the</strong>n<br />

feeded SDBS; thirdly, added SDBS into buffer solution and<br />

<strong>the</strong>n added AO to mix <strong>the</strong>m evenly. The result showed that<br />

<strong>the</strong>I RRS <strong>of</strong> <strong>the</strong> second adding sequence maximized, and so, we<br />

selected <strong>the</strong> reagent adding sequence <strong>of</strong> AO – buffer solution –<br />

SDBS.<br />

3.4. Standard curve<br />

Under <strong>the</strong> optimal condition <strong>of</strong> <strong>the</strong> experiment, plotted <strong>the</strong><br />

standard curve. Put 5.00 × 10 −4 mol L −1 SDBS into 10 mL colorimeter<br />

tube, and <strong>the</strong>n measured its intensity <strong>of</strong> <strong>scattering</strong> <strong>light</strong><br />

in terms <strong>of</strong> <strong>the</strong> test <strong>method</strong>. The result was shown in Table 1.<br />

After being compared with o<strong>the</strong>r <strong>method</strong>s, <strong>the</strong> linear range <strong>of</strong><br />

this study were wider than absorption spectra <strong>method</strong> [20],<br />

and <strong>the</strong> limits <strong>of</strong> <strong>determination</strong> (3σ) <strong>of</strong> this study were come<br />

up to direct measurement <strong>method</strong>s [11–15] had been reported<br />

approximately. It would be very good <strong>for</strong> applying this study to<br />

environmental water AS detection.<br />

3.5. Influence <strong>of</strong> co-existent ions<br />

With 1.00 × 10 −5 mol L −1 SDBS, we researched <strong>the</strong> influence<br />

<strong>of</strong> various co-existent matters on <strong>the</strong> <strong>determination</strong> <strong>of</strong><br />

resonance <strong>light</strong> <strong>scattering</strong> <strong>method</strong>. The relative error was no<br />

more than ±5%. The allowable quantities (mg) <strong>of</strong> <strong>the</strong> following<br />

ions or matters were respectively: Na + (1.2), K + (2.04), Mg 2+<br />

(1.0), AI 3+ (1.2), NH 4 + (3.0), Pb 2+ (0.01), Ba 2+ (1.6), Mn 2+<br />

(0.5), Co 2+ (1.6), Zn 2+ (1.2), Cu 2+ (0.4), Ca 2+ (2.0), F − (0.05),<br />

HCO 3− (2.0), EDTA (2.25), Cl − (1.9), Br − (2.5), Fe 2+ (0.2),<br />

S0 4 2− (2.5), Ag + (1.2), Hg 2+ (0.02), Ni 2+ (1.6), oxalic acid (2.0),<br />

and citric acid (5.0).<br />

3.6. Precision and detection limit<br />

Under <strong>the</strong> optimal condition <strong>of</strong> <strong>the</strong> experiment, prepared 11<br />

samples <strong>of</strong> 1.00 × 10 −5 mol L −1 SDBS in parallel, and <strong>the</strong>n conducted<br />

<strong>the</strong> precision detection after <strong>the</strong> <strong>determination</strong> by RLS<br />

<strong>method</strong>. The relative standard deviation was 3.5%. Through 11<br />

blank parallel experiments, <strong>the</strong> detection limit (see Table 1)<br />

<strong>of</strong> <strong>the</strong> RLS <strong>method</strong> was calculated by <strong>the</strong> <strong>for</strong>mula C L =3S b /k<br />

(S b represents <strong>the</strong> standard deviation <strong>of</strong> blank solution and k<br />

represents <strong>the</strong> slope <strong>of</strong> working curve).<br />

3.7. Sample analysis<br />

Sample analysed by RRS <strong>method</strong>. Water sampler was used<br />

to collect water samples at different environments. After filtering,<br />

accurately ga<strong>the</strong>r adequate water sample and adjust its pH<br />

value to 8.0 and <strong>the</strong>n re-filter it (most <strong>of</strong> heavy metal ions were<br />

subsided at pH 8.0.). Carefully heat it to compress it <strong>for</strong> five<br />

times, and determined <strong>the</strong> capacity by 5.00 mL distilled water<br />

in terms <strong>of</strong> <strong>the</strong> test <strong>method</strong>. And <strong>the</strong> calibration and recovery<br />

experiment was carried out. Working curve <strong>method</strong> was used<br />

to calculate <strong>the</strong> AS concentration in <strong>the</strong> water (by SDBS), and<br />

meanwhile, <strong>the</strong> comparison test was conducted in accordance<br />

with <strong>the</strong> current standard <strong>method</strong>—methylene-blue colorimetric<br />

<strong>method</strong>. Experiment data were handled by statistics and <strong>the</strong><br />

result was shown in Table 2. Table shows that t 0.05(10) = 2.228,<br />

and t < t 0.05(10) . To sum up, <strong>the</strong>re was no significant difference<br />

<strong>for</strong> <strong>the</strong> <strong>determination</strong> result <strong>of</strong> <strong>the</strong> two <strong>method</strong>s.<br />

Acknowledgements<br />

We are grateful <strong>for</strong> <strong>the</strong> financial support from <strong>the</strong> National<br />

Science Foundation <strong>of</strong> China under <strong>the</strong> grant 20775024 and <strong>the</strong><br />

Hunan Provincial Natural Science Foundation <strong>of</strong> China under<br />

<strong>the</strong> grant 03JJY3030.

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