Electronic Supplementary Material Ultrasensitive determination of mercury in human saliva by atomic fluorescence spectrometry based on solidified floating organic drop microextraction Chun-Gang Yuan*, Jincong Wang and Yi Jin School of Environmental Science & Engineering, North China Electric Power University, Baoding 071003, Hebei Province, P. R. China *Corresponding author: Chun-Gang Yuan, Email: chungangyuan@hotmail.com, Tel.: +86-312-7522516, Fax: +86-312-7522201 Effect of extraction temperature and time The extraction temperature influences the extraction kinetics. The mass transfer performance of analyte between hydrophilic and hydrophobic phases is related with the temperature. In order to achieve high extraction yields, effect of different extraction temperature was investigated in our experiment. The dependency of extraction recovery on the extraction temperature was investigated in the range of 15 °C to 55 °C. Effects of temperature on the extraction efficiency were illustrated in Figure S1. The results demonstrated that the extraction efficiency increased with temperature increasing from 15 °C to 35 °C and reached its maximum at 35 °C. Further increase in temperature caused a decrease in recovery, which could be interpreted by that higher temperature increased solubility of organic phase and degradation of complex. In our study, 35 °C was adequate to achieve quantitative 1 extraction and was chosen as the optimized equilibration temperature. The equilibration time is also regarded as an important parameter affecting on the extraction efficiency during the extraction procedure. It is desirable to complete extraction with high efficiency and speed by using shorter extraction time. However, adequate extraction time should be employed to make sure the equilibrium between the aqueous and the organic phase is reached. To evaluate the effect of equilibration time on extraction efficiency, the time range of 0.5-20 min was employed for investigation. The influence of equilibration time on extraction efficiency was illustrated in Figure S2. The results indicated that the extraction efficiency was dependent upon the extraction time obviously. The extraction efficiency increased with the increase in time of first 2 min and remained constant up to 5 min. The results demonstrated that the extraction equilibrium could be reached very fast, which was very helpful to shorten the extraction time. The extraction efficiency decreased with the increase in time after 5 min. Thus the time of 5 min was chosen for extraction. Effect of sample volume Another important parameter which may influence the enrichment factors is sample volume. During extraction procedure, the increase in the volume ratio of aqueous phase to organic phase results in the increase in the enrichment factor. In order to evaluate the effects of sample volume on the extraction efficiency, different sample volume was applied during the extraction procedure. The sample volume varied from 20 mL to 400 mL containing 5.0 ng of Hg2+ and 100 µL of 0.06% (m/v) diethyldithiocarbamate with 60 µL of 1-undecanol. The results indicated that the extraction efficiency and recovery were quantitative in the range of 20 mL to 400 mL. Based on the maximum sample volume (400 mL) and organic phase volume (60 µL) a very high preconcentration factor (6200) could be achieved. The preconcentration factor was calculated by the ratio of volumes and extraction efficiency (93%). Considering the high preconcentration factor and the requirements of real sample analysis, 25 mL of sample volume was used in our study for convenience. 2 Effect of salt and potentially interfering ions It was reported that the physical properties of aqueous solution can be changed by the presence of dissolved salt in it [33]. The diffusion rate of the targets into the organic drop and consequently the enrichment factor can be influenced by dissolved salt in solution. In order to evaluate the possible effects of ionic strength on the extraction efficiency, the dissolved NaCl with different concentration in the range of 0.1%-5% (m/v) was investigated in our experiment. From the results, the salt addition had no significant influence on the extraction efficiency from 0.1% to 2% (m/v) NaCl concentrations. However, higher NaCl concentration than 2% (m/v) resulted in obvious decrease in recovery. The results from our experiment demonstrated that the quantitative extraction could only be obtained with the concentration of NaCl lower than 2% (m/v) and the salt addition did not benefit the extraction. Therefore, the subsequent experiments were carried out without salt addition. The effect of representative potential interfering ions was tested in our study. Different amounts of common ions were added to the tested solution containing 0.5 ng mL-1 of Hg2+. The same extraction procedure was performed. The results were summarized in Table S1 and proved that the recovery was quantitative and satisfactory in the presence of excess amount of potential interfering ions under the selected conditions. Comparison with other methods Determination of mercury in saliva samples by solidified floating organic drop microextraction in this paper was compared with the other reported methods for Hg2+ preconcentration (Table S2). The preconcentration method developed in our experiment showed a comparatively low detection limit and high enrichment factor. 3 References 10. Martinis EM, Berton P, Olsina RA, Altamirano JC, Wuilloud RG (2009) Trace mercury determination in drinking and natural water samples by room temperature ionic liquid based preconcentration and flow injection-cold vapor atomic absorption spectrometry. J Hazard Mater 167: 475 17. 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Coexisting ion ion Recovery (%) b Coexisting concentration/μg mL-1 NO3- 1000 92.8±0.1 SO42- 100 91.7±0.2 K+ 1000 92.0±0.1 Fe3+ 500 91.7±0.1 Ca2+ 500 90.8±0.2 Mg2+ 500 91.8±0.7 Cu2+ 500 86.3±0.2 Zn2+ 500 90.1±0.4 Mn2+ 500 89.6±0.3 Co2+ 500 90±3 Al3+ 10 92.9±0.3 Ni2+ 10 89.6±0.4 Pb2+ 10 87.6±0.2 a Preconcentration step: 25 mL of 0.5 ng mL-1 Hg2+, pH 2.0, 100 DDTC, 60 μL of 1-undecanol at 35 ºC, 5 min of extraction time. b Mean±standard deviation(n=3). 5 μL of 0.6% (m/v) Table S2 Comparison of the present method with other methods for Hg2+ preconcentration Preconcentration Method Detection limit (ng mL-1) RSDb (%) Sample volume (mL) Enrichment factor Ref. SFODMEa-ETAAS 0.07 3.5 25 430 [20] SPEb-CVAAS 0.16 2.2 -- -- [19] SPE-ICP-AES 0.09 3.0 -- 175 [23] SDMEc-ETAAS 0.01 4.6 -- 75 [21] LLMEd-CV-AAS 0.0023 2.8 20 36 [10] SPE-CVAFS 0.18 3.2 7 -- [17] SPE-CVAAS 0.0038 3.1 1500 500 [24] LLME-CVAAS 0.01 -- 1000 -- [25] SPE-CVAAS 0.43 2.4 100 50 [26] SFODME-CVAFS 0.0025 4.1 25 182 This work a SFODME means solid floating organic drop microextraction; b SPE means solid phase extraction; c SDME means single-drop microextraction; d LLME means liquid-liquid miroextraction; 6 1 0.8 Recovery 0.6 0.4 0.2 0 0 10 20 30 40 Temperature/ºC 50 60 Figure S1 Effect of equilibration temperature on recovery of Hg2+ (Conditions: pH 2.0, 25 mL of 0.5 ng L-1 Hg2+ solution, 100 μL of 0.6% (m/v) DDTC solution, 60 μL of 1-undecanol, 5 min of extraction time, n=3, Y-axis value “1” means “100%”) 1 0.8 Recovery 0.6 0.4 0.2 0 0 5 10 15 20 25 Time/min Figure S2 Effect of equilibration time on recovery of Hg2+ (Conditions: pH 2.0, 25 mL of 0.5 ng L-1 Hg2+ solution, 100 μL of 0.6% (m/v) DDTC solution, 60 μL of 1-undecanol, extraction at 35 ºC, n=3, Y-axis value “1” means “100%”) 7