Laser-induced thermal lens spectrometry after cloud point extraction for trace analysis of mercury in water and drug samples
Journal of Analytical Science and Technology volume 5, Article number: 39 (2014)
We have developed spectrometric determination of mercury in micro volume using laser-induced thermal lens spectrometry (LI-TLS) after cloud point extraction (CPE). TLS as a sensitive method is particularly suited for small volume samples such as that of the remained phase after CPE.
Under optimum conditions, the calibration graph was linear in the range of 1 to 50 µg L-1 with a limit of detection (LOD) of 0.2 µg L-1. The preconcentration factor of 200 was achieved for 10-mL samples containing the analyte, and relative standard deviations were lower than 4%.
Combination of LI-TLS with CPE introduced a powerful method for trace analysis of mercury. The method was successfully applied for the determination of Hg+2 in water and drug samples.
In recent years, the toxicity and effects of trace elements on human health and the environment are receiving increasing attention in pollution and nutritional studies. Mercury is considered as a chemical pollutant and has become widespread in the environment mainly as a result of anthropogenic activities (Eisler ; Pacyna and Pacyna ). It has been found that mercury accumulates itself in vital organs and tissues such as the kidney and brain. Mercury and its compounds are considered as health hazards, and reports of mercury poisoning as a result of industrial, agricultural, and laboratory exposure as well as its suicidal use are numerous.
Since mercury concentrations in waters are expected to be very low, some powerful techniques are required that a few of them show enough sensitivity. Different analytical techniques have been used for mercury determination at low concentration including cold vapor atomic absorption spectrometry (CV-AAS) (Pourreza and Ghanemi ), cold vapor atomic fluorescence spectrometry (CV-AFS) (Geng et al. ), flow injection-inductively coupled plasma-optical emission spectrometry (FI-ICP-OES) (Wuilloud et al. ), and high-performance liquid chromatography-inductively coupled plasma mass spectrometry (HPLC-ICP-MS) (Chen et al. ).
Laser-induced thermal lens spectrometry (LI-TLS) is a subgroup of photothermal spectrometry methods, which is an ultrasensitive means to measure optical absorbance. The first photothermal spectroscopic method applied for sensitive chemical analysis is thermal (photothermal) lens spectrometry (TLS) (Gordon et al. ), and the first measurement of the thermal lens effect was performed by Gordon et al. () using a simple single beam apparatus (Gordon et al. ). Thermal lens effect has been developed as a powerful analytical technique for measurement of low absorbance. The utility of the techniques has increased substantially because it has been recently demonstrated that, in addition to ultrasensitivity, the techniques are particularly suited for small volume samples (Kitamori et al. ). In fact, the combined ultrasensitivity and small volume capability make it possible to successfully use them as powerful techniques for analytical devices.
The effect of thermal lens is the result of the temperature rise, which is subsequent to absorption of optical radiation and nonradiative relaxation of the excited molecules. Due to the Gaussian profile of the excitation laser, the temperature gradient produces a refractive index gradient which is maximum at the beam center and behaves like a converging or diverging lens depending on whether dn/dT is positive or negative, respectively (Georges ; Snook and Lowe ). A steady-state condition is obtained when the rate of laser heating equals the rate of heat loss due to the thermal conductivity of the solvent and the finite temperature rise (Dovichi and Harris ; Imasaka et al. ).
The thermal lens signal is sensitive to the thermo-optical properties of the medium, namely the temperature-dependent refractive index dn/dT, the thermal conductivity k, and heat capacity Cp. In addition, the signal depends on the sample absorbance and heat yield (Piepmeier ; Bialkowski ).
Mercury in different samples is present at lower levels than the detection limits of sensitive analytical methods, and its determination is spectroscopically and chemically interfered with other major constituents. Much effort has been put to solve these difficulties by the development of various techniques. Preconcentration and separation can solve these problems and lead to a higher confidence level and easy determination of trace mercury. The classical liquid-liquid extraction and separation methods are usually time consuming and labor extensive and require relatively large volumes of high-purity solvents. The additional concern is disposal of the solvent used, which creates a severe environmental problem. Cloud point extraction (CPE) is an attractive technique that reduces the consumption and exposure to a solvent, disposal cost, and extraction time. Moreover, small volume of the surfactant-rich phase obtained through this method permits the design of extraction schemes that are simple, cheap, highly efficient, speedy, and of lower toxicity to the environment than those extractions using organic solvents (Paleologos et al. , ; Manzoori and Bavili-Tabrizi ; Chappuy et al. ; Shah and Kazi ).
Cloud point methodology was used for the extraction and preconcentration of many metal ions after the formation of complexes. These metal ions can subsequently be analyzed using analytical systems such as AAS, ETAAS, ICP, GC, HPLC, CE, spectrophotometry (Sanz-Medel et al. ; Paleologos et al. ; Martinez and Gonzalo ; Giokas et al. ; Stalikas ; Afkhami et al. ), and specially LI-TLS.
The aim of our research is to combine laser-induced thermal lens spectrometry, as a sensitive method, with cloud point extraction for determination of mercury. The connection of CPE with TLS could be a powerful analytical technique for mercury because a low volume of sample remains after CPE and the use of organic solvent enhancement in TLS.
Thermal lens spectrometer setup
A single-laser thermal lens spectrometer was designed in our laboratory (Figure 1). The optical direction was designed in a horizontal-vertical mode. In order to obtain thermal lens signal, the diode laser (532 nm, 50 mW, TEM00) was used as the pump/probe source. The laser beam was focused by an 18-cm focal length lens and passed through the micro cell located at the confocal distance. The laser beam was allowed to irradiate the sample or blocked using a chopper. After filtration, the beam intensity change was measured through a 1-mm pinhole by a photo-detector that was located at a 200-cm distance from the sample cell. An operation amplifier amplified the output signal from the photo-detector, and it was digitized by the analog to a digital converter (ADC). The digital signals were processed in a personal computer by laboratory-developed software. For each sample, the signal was derived from the average of three recordings.
The TLS technique is based on the temperature gradient that is produced in an illuminated sample by nonradiative relaxation of the energy absorbed from a TEM00 laser beam. Under CW laser excitation and weak absorbing species, the TLS signal depends on the relative changes in the laser beam center intensity. Initial signal I(0) reflects only the Beer's law response of the sample, and after sufficient time, when a steady-state temperature difference is reached, the intensity at the detector will be I(8). Then, ?I/I
P is the power of the laser, ? is the wavelength, dn/dT is the temperature coefficient of the refractive index, and k is the thermal conductivity of the solvent (Bialkowski ). This can also be rewritten as:
E represents the so-called enhancement factor compared to conventional transmission measurements. It is clear that, in addition to the sample absorbance and excitation laser power, the thermal lens signal is directly affected by the thermo-optical properties of the solvent such as the dn/dT and k values of the solvent (Dovichi and Bialkowoki ; Franko and Tran ). Nonpolar organic solvents such as benzene, carbon tetrachloride, and hexane should provide good media for thermal lens measurements owing to their high dn/dT and low k values. Conversely, water, which is the most powerful and widely used solvent in spectrochemical analysis, is considered to be the worst medium for thermo-optical techniques because it has very low dn/dT and high k values.
Reagents and apparatus
All chemicals used were of analytical reagent grade. The nonionic surfactant, Triton X-114 (Acros, Fair Lawn, NJ, USA), was used without further purification. Stock standard solution of mercury at a concentration of 1,000 mg L-1 was prepared from HgCl2 (Merck, Darmstadt, Germany). Working standard solutions were obtained through appropriate dilution of the stock standard solution. A solution of 9.9?×?10-4mol L-1dithizone (Merck) was prepared in the pure ethanol (Merck). The NaOH solution was prepared by dissolving the appropriate NaOH (Merck) amount in the high-purity water. The materials and vessels used for the trace analysis were kept in 10% nitric acid for at least 24 h and subsequently washed four times with doubly distilled water.
A thermostatic bath (IKA, Königswinter, Germany) maintained at the desired temperature was used for cloud point extraction experiments, and phase separation was performed using a centrifuge (Sigma, Seelze, Germany). A 100-µL quartz micro cell with 1-mm light path was used as a determination cell (Hellma GmbH, Müllheim, Germany).
The lack of sensitivity associated with the need for detection of micro amounts of samples is probably one of the most frequently encountered problems in trace chemical analysis. As a whole, it was shown that TLS solved these problems, because in addition to the major advantage of thermal lens spectrometry (sensitivity), it gives the possibility to analyze a very low volume of the sample (15 µL); on the other hand, the volume of the remained phase after cloud point extraction is in the micro liter range. Therefore, TLS is suitable for analysis of the remained phase after the cloud point extraction, and this combination method (CPE-LI-TLS) exhibits high enhancement factor because of the preconcentration enhancement factor in CPE and the enhancement factor of TLS. In fact, the combined ultrasensitivity and small volume capability make it possible to be successfully used as powerful techniques for analytical devices. Moreover, in this work, by using an alkaline aqueous solution, the selectivity and sensitivity of the TLS method were improved. In alkaline media, the Hg(II)-dithizone secondary (M2L2) complex is formed which has higher absorption than the ML complex and enhances the M2L2 complex to background absorption at 539 nm.
In general, this improved method provides good accuracy, recovery (95.3%), and precision. Also, it presents a detection limit of 0.2 ng mL-1 and enhancement factor of 179 compared with other determination methods. However, it seems that any other real samples which are available in low volumes, such as biological and biofluid samples, can be analyzed for their mercury contents by the proposed method.
Extraction and preconcentration procedure
Aliquots of 10.0 mL of the sample containing mercury, Triton X-114 (0.1% (w/v)), dithizone (1.96?×?10-6 mol L-1), and NaOH (0.5% (w/v)) were kept in a thermostated bath at 54°C for 6 min. Separation of the aqueous and surfactant-rich phases was accomplished by centrifugation for 5 min sat 3,500 rpm. In this condition (alkaline media), no overlapping was observed between blank and complex spectra. The supernatant aqueous phase was separated completely. Then, the surfactant-rich phase was heated to dry in the oven at 100°C to remove the remaining water. Water is a poor solvent owing to its low dn/dT and high k or Cp values; therefore, for reaching a suitable thermal lens signal, all of the water remaining in the surfactant-rich phase must be eliminated. To decrease the viscosity of the dried surfactant-rich phase and to facilitate sample handling, 50 µL of ethanol was added. The 15-µL homogenized resultant solution was introduced into the micro cell located at the thermal lens spectrometer. The thermal lens spectrometer was set at a wavelength of 532 nm and a chopper frequency of 0.55 Hz. Intensity at the detector over time was obtained during thermal lens effect for each sample, and then the thermal lens signal was calculated by Eq. 1.
Results and discussion
Selection of wavelength
The absorption spectrum of the mercury-dithizone secondary complex in the remaining phase after dissolving using ethanol was studied (Figure 2). This complex shows absorption in ?max?=?539 nm. This was well matched to the wavelength of the laser beam used (??=?532 nm).
Time of steady-state thermal lens
The steady-state thermal lens effect is due to the formation of the temperature-dependent refractive index gradient. In order to optimize the required time for the steady-state thermal lens effect, the laser beam path to the sample was continuously blocked and opened by a chopper at different frequencies. The intensity of detector output over time was evaluated for 25 µg L-1 of mercury-dithizone secondary complex after CPE at a 532-nm laser wavelength. It was found out that the frequency of 0.55 Hz (time of 1.82 s) is suitable for the steady-state condition which is favorable to build up and decay the thermal lens effect.
Optimization of experimental parameters
Because of many difficulties such as high background absorption, high CPE temperature, and unpractical complete separation of the surfactant-rich phase from aqueous solution with the use of dithizone in complexation and CPE of the mercury at neutral or acidic media, we carried out our experiments in alkaline media with the addition of NaOH solution (5% w/v) to the sample solutions prior to complexation and CPE. The addition of NaOH by acting as salting-out agent markedly facilitated the phase separation process and decreased the temperature of the cloud point, since it altered the density of the bulk aqueous phase. Moreover, the alkaline solution resulted in the Hg(II)-dithizone secondary (M2L2) complex that had higher absorption than the Hg(II)-dithizone primary complex formed in neutral solution and enhanced the Hg(II)-dithizone complex to background absorption ratio at 539 nm. This effect was examined with the addition of NaOH, ranging from 0.05 to 0.8% (w/v). As shown in Figure 3, the maximum TLS signal for Hg+2 was achieved in the 0.5% (w/v) concentration of NaOH. Moreover, the addition of a salt could markedly facilitate the phase separation process, since it altered the density of the bulk aqueous phase.
Optimal equilibration time and equilibration temperature are necessary to complete reactions and to achieve easy phase separation and preconcentration as efficiently as possible. Therefore, the change of thermal lens signal in equilibration temperature was studied within the range of 35°C to 75°C. It was found that a temperature of 54°C is adequate for extraction of Hg+2. The dependence of thermal lens signal upon equilibration time was studied in the range of 3 to 15 min, and the optimum time of 6 min was chosen as a suitable time.
The concentration of the dithizone as a chelating agent was subsequently studied for its effect on the thermal lens signal of Hg+2. The variation of the thermal lens signal over the dithizone concentration was evaluated in the range of 0.49?×?10-6 to 2.97?×?10-6 mol L-1 for 10 mL aliquots of solutions containing 25 µg L-1 Hg. A concentration of 1.96?×?10-6 mol L-1 was chosen as the optimum dithizone concentration.
The effect of Triton X-114 concentration was evaluated, and it was found that a quantitative extraction of Hg+2 can be obtained with the Triton X-114 concentration in the range of 0.025% to 0.3% (w/v). The maximum of thermal lens signal observed for the Triton X-114 concentration is higher than 0.1% (w/v). In order to achieve a good enrichment factor, 0.1% (w/v) was chosen as the optimal Triton X-114 concentration.
Figures of merit
From measurements made under the optimum conditions described above, the calibration graph was linear in the range of 1 to 50 µg L-1. The calibration equation is A?=?6.42?×?10-2C?+?11.9?×?10-2 with a correlation coefficient of 0.9957, where A is the thermal lens signal for Hg+2 in the surfactant-rich phase and C is the concentration of Hg+2(µg L-1) in the sample solution. The limit of detection, defined as CL?=?3SB/m, where CL, SB, and m are the limit of detection, standard deviation of the blank, and the slope of the calibration graph, respectively, was 0.2 µg L-1.
The reproducibility of the method was studied for five replicate determinations of Hg+2 in an aqueous sample spiked with 25 µg L-1 of Hg+2 after extractions. The relative standard deviation (RSD) was lower than 4%. The enhancement factor (calculated as the ratio of the slopes of the calibration graph with and without preconcentration) and preconcentration factor (calculated as the ratio of sample volume before and after preconcentration) were 179 and 200, respectively.
Table 1 compares the sample volume, solvent volume, enhancement factor, limit of detection, and linear dynamic range of other determination methods with LI-TLS after cloud point extraction of mercury. It shows that in comparison with other sensitive determination methods such as hydride generation atomic absorption spectrometry (HG-AAS) and cold vapor atomic absorption spectrometry (CV-AAS), the LI-TLS has lower sample volume and needed solvent volume, higher enhancement factor, and good limit of detection.
The effect of interfering ions was studied at different concentrations on the thermal lens signal of a solution containing 25 µg L-1 of each analyte. An ion was considered to interfere when its presence produced a variation in the thermal lens signal of the sample of more than 5%. Among the interfering ions tested - CO3-2, Cl-, Ca2+, SO42-, NH4+, Mg2+, K+, and Na+ at the concentration of 500 times higher than that of the Hg+2 concentration; Cr3+, Zn2+, Al3+, and Fe3+ at the concentration of 200 times higher than that of the Hg+2 concentration; and F-, Cd2+, Ni2+, Fe2+, and Pb2+ at the concentration of 80 times higher than that of the Hg+2 concentration - no interfering was observed.
To verify the accuracy of the method, the developed method was applied for the determination of Hg+2 in the soft water and physiology serum. Along with the samples, several known amounts of Hg+2 were spiked to examine the reliability of the method. For this purpose, 10 mL of each sample was preconcentrated, following the proposed procedure. The results are shown in Table 2. As shown in Table 2, the recovery of the spiked amounts was in the range of 94.2% to 101.4%, which demonstrates the reliability of the proposed method.
critical micelle concentration
cloud point extraction
cloud point temperature
cold vapor atomic absorption spectrometry
cold vapor atomic fluorescence spectrometry
flow injection-inductively coupled plasma-optical emission spectrometry
high-performance liquid chromatography-inductively coupled plasma mass spectrometry
laser-induced thermal lens spectrometry
limit of detection
Afkhami A, Madrakian T, Siampour H: Flame atomic absorption spectrometric determination of trace quantities of cadmium in water samples after cloud point extraction in Triton X-114 without added chelating agents. J Hazard Mater B 2006, 138: 269–272. 10.1016/j.jhazmat.2006.03.073
Bialkowski SE: Photothermal spectroscopy methods for chemical analysis. John Wiley, New York, Chichester; 1996.
Chappuy M, Caudron E, Bellanger A, Pradeau D: Determination of platinum traces contamination by graphite furnace atomic absorption spectrometry after preconcentration by cloud point extraction. J Hazard Mater 2010, 176: 207–212. 10.1016/j.jhazmat.2009.11.014
Chen H, Chen J, Jin X, Wei D: Determination of trace mercury species by high performance liquid chromatography–inductively coupled plasma mass spectrometry after cloud point extraction. J Hazard Mater 2009, 172: 1282–1287. 10.1016/j.jhazmat.2009.07.134
Dovichi NJ, Bialkowoki SE: Thermo-optical spectrophotometries in analytical chemistry. Crit Rev Anal Chem 1987, 17: 357–423. 10.1080/10408348708085560
Dovichi NJ, Harris JM: Laser induced thermal lens effect for calorimetric trace analysis. Anal Chem 1979, 51: 728–731. 10.1021/ac50042a034
Eisler R: Mercury hazards from gold mining to humans, plants and animals. Rev Environ Contam Toxicol 2004, 181: 139–198.
Franko M, Tran CD: Analytical thermal lens instrumentation. Rev Sci Instrum 1996, 67: 1–18. 10.1063/1.1147512
Geng W, Nakajima T, Takanashi H, Ohki A: Determination of mercury in ash and soil samples by oxygen flask combustion method-cold vapor atomic fluorescence spectrometry (CVAFS). J Hazard Mater 2008, 154: 325–333. 10.1016/j.jhazmat.2007.10.029
Georges J: A single and simple mathematical expression of the signal for cw-laser thermal lens spectrometry. Talanta 1994, 41: 2015–2023. 10.1016/0039-9140(94)00200-2
Giokas DL, Paleologos EK, Tzouwara-Karayanni SM, Karayannis MI: Single-sample cloud point determination of iron, cobalt and nickel by flow injection analysis flame atomic absorption spectrometry application to real samples and certified reference materials. J Anal At Spectrom 2001, 16: 521–526. 10.1039/b010055m
Gordon JP, Leite RCC, Moore RS, Porto SPS, Whinnery JR: Long transient effects in lasers with inserted liquids samples. Bull Am Phys Soc 1964, 9: 501.
Gordon JP, Leite RCC, Moore RS, Porto SPS, Whinnery JR: Long transient effects in lasers with inserted liquids samples. J Appl Phys 1965, 36: 3. 10.1063/1.1713919
Imasaka T, Miyaishi K, Ishibashi N: Application of the thermal lens effect for determination of iron(II) with 4,7-diphenyl-1,10-phenanthroline disulfonic acid. Anal Chim Acta 1980, 115: 407–410. 10.1016/S0003-2670(01)93187-3
Kitamori T, Takeshi M, Hibara A, Sato K: Thermal lens microscopy and microchip chemistry. Anal Chem 2004, 76: 52–60 A. 10.1021/ac041508d
Li Y, Hu B: Sequential cloud point extraction for the speciation of mercury in seafood by inductively coupled plasma optical emission spectrometry. Spectrochim Acta Part B 2007, 62: 1153–1160. 10.1016/j.sab.2007.07.005
Manzoori JL, Bavili-Tabrizi A: The application of cloud point preconcentration for the determination of Cu in real samples by flame atomic absorption spectrometry. Michrochim Acta 2002, 72: 1–7.
Martinez RC, Gonzalo ER: Surfactant cloud point extraction and preconcentration of organic compounds prior to chromatography and capillary electrophoresis. J Chromatogr A 2000, 902: 251–265. 10.1016/S0021-9673(00)00837-2
Niazi A, Momeni-Isfahani T, Ahmari Z: Spectrophotometric determination of mercury in water samples after cloud point extraction using nonionic surfactant Triton X-114. J Hazard Mater 2009, 165: 1200–1203. 10.1016/j.jhazmat.2008.09.091
Pacyna EG, Pacyna JM: Mercury emissions to the atmosphere from anthropogenic sources in Europe in 2000 and their scenarios until 2020. Sci Total Environ 2006, 370: 147–156. 10.1016/j.scitotenv.2006.06.023
Paleologos EK, Stalikas CD, Karayannis MI: An optimised single-reagent method for the speciation of chromium by flame atomic absorption spectrometry based on surfactant micelle-mediated methodology. Analyst 2001, 126: 389–393. 10.1039/b009521b
Paleologos EK, Giokas DL, Tzouwara-Karayanni SM, Karayannis MI: Micelle mediated methodology for the determination of free and bound iron in wines by flame atomic absorption spectrometry. Anal Chim Acta 2002, 458: 241–248. 10.1016/S0003-2670(01)01579-3
Paleologos EK, Giokas DL, Karayannis MI: Micelle-mediated separation and cloud-point extraction. Trends Anal Chem 2005, 24: 426–436. 10.1016/j.trac.2005.01.013
Piepmeier EH: Analytical applications of lasers. Chemical analysis. Wiley, New York; 1986.
Pourreza N, Ghanemi K: Determination of mercury in water and fish samples by cold vapor atomic absorption spectrometry after solid phase extraction on agar modified with 2-mercaptobenzimidazole. J Hazard Mater 2009, 161: 982–987. 10.1016/j.jhazmat.2008.04.043
Sanz-Medel A, Campa MRF, Gonzalez EB, Fernandez-Sanchez ML: Organised surfactant assemblies in analytical atomic spectrometry. Spectrochim Acta Part B 1999, 54: 251–287. 10.1016/S0584-8547(98)00241-9
Shah F, Kazi TG: Cloud point extraction for determination of lead in blood samples of children, using different ligands prior to analysis by flame atomic absorption spectrometry: a multivariate study. J Hazard Mater 2011, 192: 1132–1139. 10.1016/j.jhazmat.2011.06.017
Shamsipur M, Shokrollahi A, Sharghi H, Eskandari MM: Solid phase extraction and determination of sub-ppb levels of hazardous Hg+2 ions. J Hazard Mater B 2005, 117: 129–133. 10.1016/j.jhazmat.2004.07.026
Snook DD, Lowe RD: Thermal lens spectrometry. Analyst 1995, 120: 2051–2068. 10.1039/an9952002051
Song JY, Hou M, Zhang LX: Determination of mercury at trace level in natural water samples by hydride generation atomic absorption spectrophotometry after cloud point extraction preconcentration. Chin Chem Lett 2006, 17: 1217–1220.
Stalikas CD: Micelle-mediated extraction as a tool for separation and preconcentration in metal analysis. Trends Anal Chem 2002, 21: 343–355. 10.1016/S0165-9936(02)00502-2
Wuilloud JCAD, Wuilloud RG, Silva MF, Olsina RA, Martinez LD: Sensitive determination of mercury in tap water by cloud point extraction pre-concentration and flow injection-cold vapor-inductively coupled plasma optical emission spectrometry. Spectrochim Acta B 2002, 57: 365–374. 10.1016/S0584-8547(01)00393-7
Support of this investigation by the Research Council of Chemistry & Chemical Engineering Research Center of Iran (CCERCI) and Iran National Science Foundation (INSF) gratefully acknowledged.
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Shokoufi, N., Atrabi, R.J. & Kargosha, K. Laser-induced thermal lens spectrometry after cloud point extraction for trace analysis of mercury in water and drug samples. J Anal Sci Technol 5, 39 (2014). https://doi.org/10.1186/s40543-014-0039-9
- Thermal lens spectrometry
- Cloud point extraction
- Triton X-114