A simple colorimetric method has been developed for the detection of lead (Pb2+) in water samples using lipoic acidfunctionalized gold nanoparticles. The lipoic acid-functionalized gold nanoparticles are induced to aggregate in the presence of the Pb2+ which results in a change in the color of the functionalized gold nanoparticles. The change in color and the amount of Pb2+ producing the change could be monitored via UV-visible spectrophotometry. A good correlation coefficient of 0.9927 was obtained for the calibration curve of the colorimetric method. The method was applied in the determination of Pb2+ in water samples and the results compared to that of measurement carried out with Atomic Absorption Spectroscopy.
Lead; Gold nanoparticles; Lipoic acid; Sensor; Colorimetric; Absorption
Gold nanoparticles have attracted immense attention in recent years owing to their numerous application in biomedicine, electronics, catalysis, and biosensing [1-6]. The surface chemistry allows for attachments of drug and targeting agents that permits them to be used in targeted drug delivery . Their large surface area also permits them to carry a large payload of cancer drugs to cancer sites in chemotherapeutic treatments . Furthermore, the high density of the gold and its capacity to absorb X-rays makes it useful as an X-ray contrast agent . One property of gold nanoparticles that makes them suitable for sensing applications is the Surface Plasmon Resonance (SPR) . SPR occurs when electrons in the conduction band of a material simulated by an incident light oscillate collectively at the interface between negative and positive permittivity materials [9,10]. Thus, SPR makes the surface of gold nanoparticles very sensitive to external influence [11-13]. When other materials encounter the surface of the gold nanoparticles there is a shift in the plasmon band that can be monitored via UV-Vis spectrometry . The shift occurs due to the change in the effective refractive index of the medium [15,16]. The change in wavelength could also be due to plasmon coupling between the closely packed particles which occurs when the particles aggregate. This phenomenon has been exploited in the sensing of heavy metals [17,18].
Lead is one of the most toxic metals found in the environment. Lead toxicity is an important environmental hazard and its effects on the human body are devastating. It is particularly detrimental for children as exposure to lead ion has been shown to cause brain and kidney abnormalities [19,20]. The presence of Pb2+ in water bodies continue to pose a serious threat to health and the environment. Several methods have been developed for detection of lead in the past [21-24]. The present work involves the use of gold nanoparticlebased sensors in the detection of Pb2+ in water samples. Some of the unique characteristics of gold nanoparticles are exploited for the detection of lead ion in water bodies. The unique characteristics of gold nanoparticles being taken advantage of include their small size, large surface area, ability to bind with other species and the surface plasmon. Gold nanoparticles functionalized with different kinds of ligands have previously been used in the detection of heavy metals [17,18]. The mechanism of detection depends on the sensitivity to change in size, aggregation state and refractive index of the gold nanoparticles upon attachment of metal ions [25,26].
In addition to heavy metals, gold nanoparticles have also been used in sensing different materials ranging from biomolecules to electronics [15,16]. Most recently, Ratnarathorn et al.  used maleic acid as a ligand on gold nanoparticles for the detection of lead. Maleic acid has two terminal carboxylic acid groups. One of the carboxylic acids in this case, was conjugated to the gold nanoparticle and the other to the lead ion. Nevertheless, the interaction between gold nanoparticles and carboxylic acids is not strong and thus the functionalized particles tend to be unstable. Ligands with thiol or sulfur terminal groups form strong bonds with gold nanoparticles and ensure the stability of the resulting nanoparticles.
Absorption spectroscopy was carried out with UV-3600 Plus from Shimadzu, MD, USA. Transmission Electron Microscopy (TEM) images were acquired on JEM-1400 PLUS (JEOL USA, Peabody, Massachusetts, USA). The images were viewed using Digital Micrograph software from GATAN (GATAN Inc., Pleasanton, CA, USA). For comparison purposes, the Pb content was also analyzed by Atomic Absorption Spectrometry (AAS) from PerkinElmer Corporation, Waltham, MA, USA). Dynamic Light Scattering (DLS) measurements were carried out using Horiba Particle Size Analyzer LB 550 from Horiba Instruments Inc., Irvine, CA, USA.
Synthesis of gold nanoparticles
Synthesis of citrate-stabilized GNPs was carried out using a modified Frens method [28-30]. First, a 100 mL of 0.6 mM gold salt solution in a 250 mL Erlenmeyer flask equipped with a magnetic stirring bar was brought to boil on a hotplate. To this solution, 2 mL of 0.17 M sodium was added and the solution further stirred for another 15 minutes. A series of color changes, from light yellow to gray, to purple, and to ruby red was observed. The synthesized gold nanoparticles were characterized using the UV-Vis, DLS, and TEM.
Ligand exchange reaction
The ligand exchange reaction was then carried out in order to replace citrate molecules with lipoic acid. The amount of lipoic acid used was based on the size of the gold nanoparticles as determined by dynamic light scattering measurements. Using the diameter of the gold nanoparticles, the surface of the gold nanoparticle and the number of ligands that could be attached to the surface of the gold nanoparticles were computed. Lipoic acid was used in excess to ensure complete exchange of the ligand. Specifically, 250 times excess of ligands was used to guarantee complete exchange of the citrate molecules. The reaction was also carried out under basic conditions (pH = 10) to ensure complete deprotonation of the carboxylic acid groups on the lipoic acid. To carry this out, 0.24 g of the lipoic acid was dissolved in basic water, added to the gold nanoparticles and allowed to stir at room temperature overnight. The particles were then purified by a series of centrifugation and the pellets dispersed in pure water for analysis.
In this study, the concentration of Pb ions in water samples was assessed by a colorimetric method using gold nanoparticles and the results compared with measurements carried out by Atomic Absorption Spectroscopy. Gold nanoparticles were first synthesized by the citrate method followed by a ligand exchange reaction to replace the citrate molecules as illustrated in Figure 1. The lipoic acid used as a ligand has a disulfide group at one end for attachment to the gold surface and a carboxylic acid at the other end for interaction with the Pb ions. Interaction with the Pb ion induces aggregations resulting in a change of color as displayed in Figure 2. It was observed that the ruby red color of the gold nanoparticles changes to a purple color upon the addition of lead ions to the gold nanoparticle solution.
Figure 1: Mechanism behind colorimetric detection of Lead ions.
Figure 2: Gold Nanoparticle solution with different concentrations of lead ions.
Dynamic light scattering studies
The functionalized gold nanoparticles were characterized using dynamic light scattering (DLS) measurements. The DLS is a particle size analyzer that evaluates the size and size distribution of nanomaterials in solution. The size determined via DLS is usually bigger than that determined via Transmission Electron Microscope (TEM) imaging since DLS measures the hydrodynamic diameter which comprises of the particles itself and a kind of an electric dipole layer that sticks to the surface of particles in solution. TEM, on the other hand, measures the diameter of the exact image of the particles thus yielding more precise values. The DLS spectra of the citrate-stabilized gold nanoparticles (GNP-Citrate) and that of the corresponding lipoic acid coated gold nanoparticles (GNPLA) are displayed in Figure 3. The average size of the citrate state stabilized gold nanoparticles were found to be 20.6 nm and that of the functionalized particles was 21.5 nm.
Figure 3: Dynamic Light Scattering measurement of gold nanoparticle before and after functionalization with lipoic acid.
Transmission electron microscopy imaging
The morphology of the lipoic acid conjugated gold nanoparticle (GNP-LA) was analyzed before and after interaction with lead ions using Transmission electron microscopy (TEM). The gold nanoparticles before conjugation with Pb ion show the particles to be uniformly dispersed with negligible aggregation. The TEM image of the lipoic acid conjugated gold nanoparticle along with the histogram of the size analysis is displayed in Figure 4. The uniformity of the size and shape of the lipoic acid conjugated gold nanoparticle before interaction with Pb ions is clearly demonstrated in Figure 4a. The average size of the functionalized gold nanoparticles as displayed in the histogram in Figure 4b is 13.10 nm. Figures 4c and 4d show the TEM images of the lipoic acid conjugated gold nanoparticles with the lead ions (GNP-LAPb). The average size of these particles was 13.90 nm which is about 0.8 nm bigger than the size of just lipoic acid functionalized gold nanoparticles. The increase in size suggests that the Pb2+ ions interacted with the carboxylic groups of the lipoic acid bound to the gold nanoparticles. It can also be observed in the TEM images that the gold nanoparticles with the Pb ions are more clustered, which indicates that the lead ions cause the gold nanoparticles to aggregate.
Figure 4: TEM image of gold nanoparticles before and after conjugation with Pb ions. (a) GNP-LA; b) corresponding histogram of GNP-LA-Pb; (c and d) GNP-LA-Pb at different magnifications.
The synthesized gold nanoparticles before and after the ligand exchange reaction were further characterized by UV-Vis Spectroscopy. The characterization was carried out to assess the functionalization of the gold nanoparticles with the lipoic acid. Gold nanoparticles exhibit SPR, which is the collective oscillation of conduction band electrons in resonance with an incident light of a specific wavelength. The SPR of gold nanoparticles result in the absorption of light of wavelength between 500 nm and 600 nm depending on the size and shape of the nanoparticles. Thus, any changes on the surface of the gold nanoparticles results in the shift of the plasmon band, which can be monitored by UV-Vis Spectroscopy. An increase in size of the gold nanoparticle through aggregation or through binding with ligands results in a red shift of the Plasmon band. The UV-Vis spectra of the gold nanoparticles before and after the ligand exchange reaction is displayed in Figure 5. The surface plasmon band of the bare gold nanoparticles was 518 nm and this was red-shifted to 523 nm upon addition of the lipoic acid. A shift in the peak absorbance is indicative of a gold nanoparticle surface modification. In this case, it signifies the exchange of the lipoic acid with the citrate molecules.
Figure 5: UV-Vis measurement of the lipoic acid functionalized gold nanoparticles before and after ligand exchange.
To prepare a calibration for the colorimetric detection of lead ions using UV-Vis, a series of solutions with different concentration of lead ions were prepared. The lead solutions with concentration within the range of 1 to 20 ppm were added to the prepared lipoic acid coated gold nanoparticles and tested with UV-VIS spectrometer. Briefly, 1 mL of GNP-LA solution was added to 1 mL of a Pb2+ ion solution of a known concentration. The GNP-LA turned purple as they met Pb2+ at high ionic strength, indicating the formation of aggregates. Figure 6 shows the UV-Vis spectra of gold nanoparticle solutions with different concentrations of lead ions. It was observed that the higher the concentration of the lead ions the greater the degree of aggregation of the gold nanoparticles. The wavelength of the plasmon band in the absence of the lead ions is 523 nm but a red shift of plasmon band is observed with each increase in the concentration of the lead ions. Thus, a linear relationship was found to exist between the concentration of lead ions and aggregation of gold nanoparticles in the contact with the lead ions. The colorimetric detection of aqueous Pb2+ was performed at room temperature.
Figure 6: UV-Vis spectra of gold nanoparticle solutions with different concentration of lead ions.
From the data of the UV-Vis, a curve of absorbance at 620 nm over the absorbance at 523 nm were computed and plotted over the concentration of lead in the solution. The correlation coefficient of this curve was 0.9927 as displayed in Figure 7. The calibration was then used to determine the concentration of Pb in water samples. At lower concentration of the lead the change in absorbance at 523 nm and 620 nm is low but at a higher concentration of lead, this change becomes more drastic. The curve is therefore linear at a higher concentration of lead than at a lower concentration of the same.
Figure 7: Calibration Curve for absorbance versus concentration of lead ions.
Atomic absorption spectrometry
Atomic Absorption Spectrometric measurements were also carried out to compare the results obtained by the gold nanoparticle detection method. Standards were prepared and used in the construction of the calibration curve for the atomic absorption measurements. Various solutions with different concentrations of lead, ranging from 1 to 25 ppm, were prepared. In all the solutions, nitric acid was added to enhance the amount of lead available for measurement. The correlation coefficient of the curve was 0.9998 as displayed in Figure 8. Next, water samples with varying amounts of lead were also measured using the calibration curve and the absorbance was correlated to the graph to determine the respective concentration. This data was then compared to that of the UV-Vis method employing the gold nanoparticle probe.
Figure 8: The calibration curve for atomic absorption analysis of lead.
Analysis of lead in watersheds
The colorimetric detection method was applied in the determination of lead in water samples drawn from liberty watershed, one of the three sheds that supply drinking water for the city of Baltimore (MD). Samples were taken over three different seasons (Summer 2018, Fall 2018 and Spring 2019) to see if Pb concentration changes with the seasons. Following the recommended protocol for sample preparation, Pb concentration was measured using AAS. It was observed that Pb2+ions detected in the water samples were negligible. To confirm the application of our colorimetric method, the samples were spiked with Pb2+ ions standard and tested. The concentration of Pb2+ ions in the water samples was 24 ppm, 12 ppm, and 4 ppm, respectively. All the measurements were conducted in triplicate and the values shown are averages. The results obtained for both the colorimetric testing with the gold nanoparticles using UV-Vis produced similar results as displayed in Table 1, indicating that the colorimetric detection method is suitable for testing lead in water bodies.
|Water samples||Concentration of Pb2+ (ppm)|
|Colorimetric method||AAS method|
|Summer 2018 #2||4.17 ± 0.25||4.27 ± 0.06|
|Fall 2018 #2||10.65 ± 1.13||11.16 ± 0.91|
|Spring 2019 #2||24.03 ± 1.0||24.37 ± 0.50|
Table 1:Determination of Pb ions in three different watersheds using both the colorimetric method and the AAS method.
Gold nanoparticles capped with lipoic acid were prepared using the Frens method of synthesis followed by ligand exchange reaction to replace citrate molecules with lipoic acid. The prepared particles were characterized using UV-Vis spectrometry, and Dynamic Light Scattering. The gold nanoparticle capped-lipoic acid was subsequently developed into a sensor capable of detecting lead ion in water. The lead ions interacted with the lipoic acid in solution which resulted in the aggregation of the particles to the degree of the concentration of the lead in solution. The morphology of the gold nanoparticles upon interaction with the lead was also examined using transmission electron microscopy. The results from Atomic Absorption Spectrometry corroborated with that of the gold nanoparticle sensor. The correlation coefficient of the calibration of the colorimetric method was 0.9927. The method was successfully used to determine the lead concentration of water samples collected from Liberty watershed (one of the three sheds that supply drinking water for the city of Baltimore) over three seasons. The method thus provides a quick alternative technique for the detection and quantification of lead in water bodies and to the best of knowledge, constitutes a new colorimetric method for lead detection.
This study was funded by the University of Maryland System (Wilson E. Elkins Professorship), Constellation, an Exelon Company (E2- Energy to Educate grant program) and the United States Department of Education (USDE-SAFRA Title III Grant). The authors extend special thanks to the office of Institutional Advancement, Coppin State University, for administrative support. The content is exclusively the responsibility of the authors and does not necessarily represent the official views of the funding agencies. The authors also acknowledge research support from the National Institutes of Health (NIH) grant RO1CA206190 to MMA.
Citation: Ghann W, Harris T, Kabir D, Kang H, Jiru M, et al. (2019) Lipoic Acid Decorated Gold Nanoparticles and Their Application in the Detection of Lead Ions. J Nanomed Nanotech. 10:539. doi: 10.35248/2157-7418.104.22.1689
Received Date: Nov 19, 2019 / Accepted Date: Dec 05, 2019 / Published Date: Dec 12, 2019
Copyright: © 2019 Ghann W, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.