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Spectrochimica Acta Part A 71 (2008) 398–402<br />

<strong>Resonance</strong> <strong>light</strong> <strong>scattering</strong> <strong>method</strong> <strong>for</strong> <strong>the</strong> <strong>determination</strong> <strong>of</strong><br />

<strong>anionic</strong> surfactant with acridine orange<br />

Xilin Xiao a,b , Yongsheng Wang a,∗ , Zhangming Chen c , Qiangxiang Li d , Zhihuo Liu d ,<br />

Guirong Li a , Changyin Lü a , Jinhua Xue a , Yanzhi Li a<br />

a College <strong>of</strong> Public Health, University <strong>of</strong> South China, Hengyang 421001, PR China<br />

b College <strong>of</strong> Chemistry and Chemical Engineering, University <strong>of</strong> South China, Hengyang 421001, PR China<br />

c Changsha Medical College, Changsha 410219, PR China<br />

d Xiangya Hospital, Central South University, Changsha 410219, PR China<br />

Received 3 December 2007; received in revised <strong>for</strong>m 27 December 2007; accepted 1 January 2008<br />

Abstract<br />

The resonance Rayleigh <strong>scattering</strong> (RRS), second-order <strong>scattering</strong> (SOS) and frequency-double <strong>scattering</strong> (FDS) spectra <strong>of</strong> sodium dodecylbenzene<br />

sulfonate (SDBS) (<strong>anionic</strong> surfactant (AS)) with acridine orange (AO) system were studied. Experimental results showed that when<br />

λ em = λ ex = 537 nm, <strong>the</strong> RRS peak <strong>of</strong> AO was greatly enhanced with <strong>the</strong> increase <strong>of</strong> SDBS concentration at a pH range <strong>of</strong> 1.8–4.0. The linear range<br />

<strong>of</strong> <strong>the</strong> calibration curve <strong>for</strong> SDBS was 0.028–8.71 mg L −1 with a detection limit <strong>of</strong> 8.36 gL −1 when <strong>the</strong> AO concentration was 2.5 × 10 −5 mol L −1 .<br />

The <strong>method</strong> has been applied to <strong>the</strong> <strong>determination</strong> <strong>of</strong> trace amount <strong>of</strong> AS in environmental water samples with satisfactory results. In addition,<br />

when λ em = 321 nm and λ ex = 642 nm, <strong>the</strong> intensity <strong>of</strong> FDS was proportional to <strong>the</strong> SDBS concentration ranging from 0.014 to 8.71 mg L −1 and <strong>the</strong><br />

correlation coefficient was 0.993 with a detection limit <strong>of</strong> 4.31 gL −1 ; when λ em = 642 nm and λ ex = 321 nm, <strong>the</strong> intensity <strong>of</strong> SOS was proportional<br />

to <strong>the</strong> SDBS concentration ranging from 0.050 to 8.71 mg L −1 , and <strong>the</strong> correlation coefficient was 0.993 with a detection limit <strong>of</strong> 14.9 gL −1 .<br />

© 2008 Elsevier B.V. All rights reserved.<br />

Keywords: Anionic surfactant; Acridine orange; <strong>Resonance</strong> Rayleigh <strong>scattering</strong>; <strong>Resonance</strong> nonlinear <strong>scattering</strong><br />

1. Introduction<br />

With <strong>the</strong> extensive application <strong>of</strong> syn<strong>the</strong>tic detergent in daily<br />

life, <strong>the</strong> analysis <strong>of</strong> trace <strong>anionic</strong> surfactant (AS) in water<br />

has become an indispensable topic [1] in <strong>the</strong> environmental<br />

monitoring. In recent years, most <strong>of</strong> resonance <strong>light</strong> <strong>scattering</strong><br />

technologies had been applied to <strong>the</strong> research <strong>of</strong> biologic<br />

molecule such as protein [2–5] and nucleic acid [6–10], and<br />

<strong>the</strong> huge advantage and potential application value had been<br />

embodied and shown. In order to overcome <strong>the</strong> disadvantages<br />

<strong>of</strong> methylene-blue colorimetric <strong>method</strong> that needs <strong>the</strong> organic<br />

agent <strong>for</strong> its extraction and <strong>of</strong> tedious operation, <strong>the</strong> direct measurement<br />

<strong>of</strong> AS in <strong>the</strong> environmental water samples by <strong>the</strong> water<br />

phase was reported [11–15], but <strong>the</strong> <strong>Resonance</strong> <strong>light</strong> <strong>scattering</strong><br />

<strong>method</strong> <strong>for</strong> <strong>the</strong> direct <strong>determination</strong> <strong>of</strong> <strong>anionic</strong> surfactant with<br />

acridine orange was not reported so far. No need <strong>of</strong> organic agent<br />

∗ Corresponding author. Tel.: +86 734 8280312.<br />

E-mail addresses: xiaoxl2001@163.com (X. Xiao),<br />

yongsheng.w@tom.com (Y. Wang).<br />

<strong>for</strong> <strong>the</strong> extraction <strong>for</strong> <strong>the</strong> new <strong>method</strong> mentioned in this <strong>the</strong>sis<br />

and <strong>the</strong> operation was simple and quick and <strong>the</strong> sensitivity was<br />

high. This <strong>method</strong> had been applied to <strong>the</strong> <strong>determination</strong> <strong>of</strong> AS<br />

in <strong>the</strong> water environment, with a satisfactory result.<br />

2. Experimental<br />

2.1. Main instruments and reagent<br />

970 CRT spectr<strong>of</strong>luorophotometer (Shanghai Sanco Instruments<br />

Co. Ltd.), UV8500 ultraviolet visible range spectrophotometer<br />

(Shanghai Techcomp Holding Ltd.), PB-20 standard pH<br />

meter (Sartorius Scientific Instruments (Beiing) Co. Ltd.), and<br />

AB204-S electronic analytical balance (Mettler-Toledo Instruments<br />

(Shanghai) Co. Ltd.) were used in this experiment.<br />

Sodium dodecyl benzene sulfonate (SDBS, analytic reagent,<br />

China National Medicine Group Shanghai Chemical Reagent<br />

Company) standard solution: <strong>the</strong> concentration <strong>of</strong> stock<br />

solution was 5.00 × 10 −3 mol L −1 , concentration <strong>of</strong> working<br />

solution was 5.00 × 10 −4 mol L −1 , concentration <strong>of</strong> AO solu-<br />

1386-1425/$ – see front matter © 2008 Elsevier B.V. All rights reserved.<br />

doi:10.1016/j.saa.2008.01.002


tion was 5.00 × 10 −3 mol L −1 , which was diluted into <strong>the</strong><br />

working solution <strong>of</strong> 5.00 × 10 −4 mol L −1 , Tris(hydroxymethyl)<br />

aminomethane buffer solution: 0.1 mol L −1 , which was mixed<br />

by Tris and 0.1 mol L −1 HCl. The remaining reagents were all<br />

analytic reagent, and experiment water adopted <strong>the</strong> secondary<br />

distilled water.<br />

2.2. Experiment <strong>method</strong><br />

X. Xiao et al. / Spectrochimica Acta Part A 71 (2008) 398–402 399<br />

2.2.1. Determination <strong>of</strong> resonance Rayleigh <strong>scattering</strong><br />

Added 0.50 mL AO solution and 0.50 mL Tris buffer solution<br />

(pH2.0) into <strong>the</strong> 10 mL colorimeter tube, joggled <strong>the</strong> tube<br />

to mix <strong>the</strong> solutions evenly, and <strong>the</strong>n added certain SDBS standard<br />

solution or sample solution, and joggled <strong>the</strong> tube after <strong>the</strong><br />

solutions were diluted behind <strong>the</strong> scale. Put <strong>the</strong> mixed solution<br />

at <strong>the</strong> place <strong>of</strong> λ em = λ ex <strong>for</strong> synchronous scanning, and <strong>the</strong>n <strong>the</strong><br />

resonance Rayleigh <strong>scattering</strong> (RRS) spectrum can be obtained.<br />

Measured <strong>the</strong> <strong>scattering</strong> <strong>light</strong> intensity at <strong>the</strong> 537 nm <strong>of</strong> <strong>the</strong> RRS<br />

peak, marked it as I 1 ; meanwhile measured <strong>the</strong> <strong>scattering</strong> <strong>light</strong><br />

intensity <strong>of</strong> reagent blank, marked it as I 0; I RRS = I 1 − I 0. Both<br />

excitation slit width and emission slit width were all 5.0 nm.<br />

2.2.2. Determination <strong>of</strong> resonance nonlinear <strong>scattering</strong><br />

Used <strong>the</strong> <strong>method</strong> <strong>of</strong> above Section 2.2.1 to make <strong>the</strong> test<br />

solution, and used λ em = 1/2λ ex and λ em =2λ ex to measure <strong>the</strong><br />

intensities I FDs (frequency-double <strong>scattering</strong>) and I SOS (secondorder<br />

<strong>scattering</strong>) <strong>of</strong> two resonance nonlinear <strong>scattering</strong> <strong>light</strong>s.<br />

FDS and SOS spectrograms can be made by plotting <strong>the</strong> corresponding<br />

wavelengths <strong>of</strong> I FDs and I SOS . Measured <strong>the</strong> <strong>scattering</strong><br />

intensities I FDs and I SOS <strong>of</strong> ion-associated complex at FDS peak<br />

and SOS peak as well as <strong>the</strong> <strong>scattering</strong> intensities IFDs 0 and<br />

ISOS 0 <strong>of</strong> reagent blank, <strong>the</strong>n ΔI FDs = I FDs − IFDS 0 and ΔI SOS =<br />

I SOS − ISOS 0 . Excitation slit width and emission slit width were<br />

both 5.0 nm.<br />

3. Results and discussion<br />

Fig. 1. <strong>Resonance</strong> Rayleigh <strong>scattering</strong> spectra <strong>of</strong> AO–SDBS system at pH<br />

2.0: SDBS, (2); AO, (3); AO–SDBS ((AO): 1.00 × 10 −5 mol L −1 ; (SDBS):<br />

1.00 × 10 −5 mol L −1 ).<br />

ence and accordingly increase <strong>the</strong> RRS strength. There<strong>for</strong>e, this<br />

experiment adopted λ em = λ ex = 537 nm as <strong>the</strong> study wavelength.<br />

From <strong>the</strong> absorption spectrogram, we saw that, with <strong>the</strong> gradual<br />

increase <strong>of</strong> adding quantity <strong>of</strong> SDBS, absorbance <strong>light</strong> <strong>of</strong> AO<br />

at 490 nm constantly reduced, this was because that AO reacted<br />

with SDBS to generate <strong>the</strong> ion-associated complex. The reason<br />

that RRS signal increases may be that positive ion dye stuffs AO<br />

and SDBS in <strong>the</strong> water solution generated <strong>the</strong> ion-associated<br />

complex through <strong>the</strong> reactions such as water repellent, electrostatic<br />

reaction or charge transfer complex [16], resulted in <strong>the</strong><br />

enhancement <strong>of</strong> RRS signal intensity at 537 nm.<br />

Mole-ratio <strong>method</strong> was used to study <strong>the</strong> composition <strong>of</strong> ionassociated<br />

complex: fixed SDBS concentration, changed <strong>the</strong> AO<br />

concentration, measured and determined <strong>the</strong> I RRS <strong>of</strong> corresponding<br />

reagent blanks and various solution groups at 537 nm,<br />

plotted <strong>the</strong> I–V diagram. Result showed that a turning point<br />

occurred in case <strong>of</strong> mole ratio 1.2:1 <strong>for</strong> AO and SDBS, namely,<br />

3.1. <strong>Resonance</strong> Rayleigh <strong>scattering</strong> spectra properties <strong>of</strong><br />

SDBS–AO system<br />

The experimental <strong>method</strong> was used to measure <strong>the</strong> RRS spectrum<br />

<strong>for</strong> AO–SDBS system, as shown in Figs. 1 and 2 was <strong>the</strong><br />

ultraviolet-visible range spectrum <strong>for</strong> AO–SDBS system. From<br />

Fig. 1, we knew that <strong>the</strong> RRS signals <strong>of</strong> SDBS and AO were<br />

both weaker. AO had a stronger resonance Rayleigh <strong>scattering</strong><br />

signal near 512 nm, which was corresponding to <strong>the</strong> wide peak<br />

valley <strong>of</strong> ultraviolet-visible spectrum at 520 nm. With <strong>the</strong> addition<br />

<strong>of</strong> SDBS, stronger RRS peaks occurred at both 337 nm<br />

and 537 nm. The two RRS peaks (337 nm and 537 nm) in <strong>the</strong><br />

RRS spectra was on <strong>the</strong> right <strong>of</strong> corresponding absorption peak,<br />

this was a characteristic “absorption-<strong>scattering</strong>” phenomenon<br />

<strong>of</strong> RRS spectra. Compared to RRS signal <strong>of</strong> acridine orange,<br />

RRS signal at 537 nm was stronger than that at 337 nm. If measuring<br />

<strong>the</strong> signal at <strong>the</strong> stronger wavelength, it may not only<br />

avoid <strong>the</strong> adverse reaction from <strong>the</strong> higher radiant energy <strong>of</strong><br />

short wavelength, but also reduced <strong>the</strong> background interfer-<br />

Fig. 2. Absorption spectra <strong>of</strong> AO–SDBS system at pH 2.0: (AO),<br />

1.00 × 10 −5 mol L −1 ; (SDBS)/×10 −5 mol L −1 ; (1) 0.00; (2) 0.25; (3) 0.50; (4)<br />

0.75; (5) 1.00; (6) 1.25.


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

Fig. 3. Spectra <strong>of</strong> frequency-double <strong>scattering</strong> (FDS) <strong>for</strong> SDBS–AO system:<br />

(1) 0.20 mL AO; (2) 1 + 0.20 mL SDBS; (3) 1 + 0.40 mL SDBS ((AO):<br />

5.00 × 10 −4 mol L −1 ; (SDBS): 5.00 × 10 −4 mol L −1 ).<br />

<strong>the</strong> composition ratio <strong>of</strong> AO and SDBS in <strong>the</strong> ion-associated<br />

complex is 1.2:1. In case <strong>of</strong> any change <strong>of</strong> SDBS concentration,<br />

its ratio changed too, and this was because that <strong>the</strong>re was<br />

a ratio difference between AO monomer and dimer, which was<br />

identical to <strong>the</strong> study <strong>of</strong> He et al. [17].<br />

3.2. <strong>Resonance</strong> nonlinear <strong>scattering</strong> spectra properties <strong>of</strong><br />

SDBS–AO system<br />

When incident ray <strong>of</strong> different wavelengths passed through<br />

<strong>the</strong> reagent blank and solution <strong>of</strong> ion-associated complex, we<br />

recorded <strong>the</strong> <strong>scattering</strong> <strong>light</strong> intensity <strong>of</strong> incident ray at places<br />

<strong>of</strong> 1/2 or tow times wavelength, and plotted <strong>the</strong> corresponding<br />

wavelength diagrams according to <strong>scattering</strong> <strong>light</strong> intensity,<br />

and <strong>the</strong>n we could get <strong>the</strong> spectrograms <strong>of</strong> FDS and SOS<br />

(Figs. 3 and 4). From <strong>the</strong> two figures, we saw that: (1) in FDS<br />

spectrum, when λ em = 321 nm and λ ex = 642 nm, I FDs maximized,<br />

and it was proportional to <strong>the</strong> matter concentration in<br />

<strong>the</strong> solution under certain condition. In SOS spectrum, when<br />

λ em = 642 nm and λ ex = 321 nm, I SOS maximized, and it was<br />

proportional to <strong>the</strong> matter concentration in <strong>the</strong> solution under<br />

certain condition. (2) FDS and SOS <strong>of</strong> acridine orange were<br />

both weak. When adding <strong>the</strong> SDBS into acridine orange to generate<br />

<strong>the</strong> ion-associated complex, <strong>the</strong> FDS and SDBS enhanced<br />

greatly. FDS maximum peak <strong>of</strong> ion-associated complex was at<br />

321 nm and SOS maximum peak was at 642 nm. FDS maximum<br />

peak wavelength was 1/2 <strong>of</strong> SOS maximum peak wavelength.<br />

The radiation peak occurred near 542 nm should be <strong>the</strong> fluorescence<br />

peak [18], and <strong>the</strong>re<strong>for</strong>e, <strong>the</strong>re was a similarity between<br />

FDS peak and SOS peak. (3) I FDs > I SOS , FDS had a higher<br />

sensitivity and FDS used <strong>the</strong> long wavelength <strong>of</strong> low energy as<br />

<strong>the</strong> incident ray, which was more beneficial to determining some<br />

systems that are easy to generate <strong>the</strong> photochemical reaction. As<br />

a result, FDS was preferred <strong>for</strong> <strong>the</strong> <strong>determination</strong> study under<br />

<strong>the</strong> general condition.<br />

Fig. 4. Spectra <strong>of</strong> second-order <strong>scattering</strong> (SOS) <strong>for</strong> SDBS–AO system:<br />

(1) 0.20 mL AO; (2) 1 + 0.20 mL SDBS; (3) 1 + 0.40 mL SDBS ((AO):<br />

5.00 × 10 −4 mol L −1 ; (SDBS): 5.00 × 10 −4 mol L −1 ).<br />

FDS and SOS were all nonlinear <strong>scattering</strong>s caused from<br />

<strong>the</strong> resonance <strong>scattering</strong>. The above experiment results showed<br />

that <strong>the</strong> resonance nonlinear <strong>scattering</strong> and resonance Rayleigh<br />

<strong>scattering</strong> <strong>of</strong> AO itself were all weaker. After adding SDBS,<br />

<strong>the</strong> three <strong>scattering</strong>s were all greatly enhanced and were in a<br />

linear relation with <strong>the</strong> added quantity. There<strong>for</strong>e, <strong>the</strong>re was a<br />

correlation between RRS and <strong>the</strong> two <strong>scattering</strong>s, which synchronously<br />

change with <strong>the</strong> generation and changes <strong>of</strong> RRS. The<br />

increase <strong>of</strong> molecular polarizability was an important factor [19]<br />

<strong>for</strong> <strong>the</strong> enhancement <strong>of</strong> RRS, and <strong>the</strong> sharp increase <strong>of</strong> molecular<br />

polarizability however was exactly <strong>the</strong> important condition <strong>for</strong><br />

generating <strong>the</strong> nonlinear <strong>scattering</strong>s such as frequency-double<br />

<strong>scattering</strong>, second-order <strong>scattering</strong>, etc. There<strong>for</strong>e, a stronger<br />

interdependent relationship may be existed among <strong>the</strong>m.<br />

3.3. Experiment <strong>of</strong> condition optimization<br />

The experiment <strong>of</strong> condition optimization was made on <strong>the</strong><br />

basis <strong>of</strong> RRS <strong>method</strong>.<br />

3.3.1. Influence <strong>of</strong> acidity<br />

Used <strong>the</strong> experimental <strong>method</strong> and took “Tris–HCl and<br />

Tris–NaOH” buffer solution to adjusted pH value <strong>of</strong> this solution,<br />

we determined <strong>the</strong> RRS intensity under different acidities<br />

and <strong>the</strong> intensity was among <strong>the</strong> range <strong>of</strong> pH 1.8–4.0, and I <strong>of</strong><br />

this system maximized and kept <strong>the</strong> constant value. Hence, this<br />

experiment selected Tris buffer solution at pH 2.0 to control <strong>the</strong><br />

acidity <strong>of</strong> <strong>the</strong> solution.<br />

3.3.2. Influence <strong>of</strong> dosage <strong>of</strong> acridine orange<br />

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

<strong>of</strong> dosage <strong>of</strong> acridine orange, and <strong>the</strong> result showed that<br />

when AO dosage was 0.50 mL, <strong>the</strong> resonance <strong>light</strong> <strong>scattering</strong> <strong>of</strong><br />

this system enhanced maximally.


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.


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

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