Single particle analysis using the Agilent 7700x ICP-MS

Similar documents
TITLE NANOPARTICLE SUSPENSIONS COUNTING AND SIZING NANOPARTICLES VIA SINGLE PARTICLE INDUCTIVELY COUPLED PLASMA MASS SPECTROMETRY

Enhancing the productivity of food sample analysis with the Agilent 7700x ICP-MS

Characterization of nanoparticles in aqueous samples by ICP-MS

The ultratrace determination of iodine 129 in aqueous samples using the 7700x ICP-MS with oxygen reaction mode

High-Speed Environmental Analysis Using the Agilent 7500cx with Integrated Sample Introduction System Discrete Sampling (ISIS DS)

A Comparison of Microsecond vs. Millisecond Dwell Times on Particle Number Concentration Measurements by Single Particle ICP-MS

Accurate analysis of neptunium 237 in a uranium matrix, using ICP-QQQ with MS/MS

Lead isotope analysis: Removal of 204 Hg isobaric interference from 204 Pb using ICP-QQQ in MS/MS mode

Multi-Element Analysis of Petroleum Crude Oils using an Agilent 7900 ICP-MS

SP-ICP-MS Analysis of Size and Number Concentration in Mixtures of Monometallic and Bimetallic (Core-shell) Nanoparticles

Agilent s Solutions for Nanoparticles Analysis ICP-MS, ICP-MS/MS, software. Alain Desprez Agilent Technologies

Direct Measurement of Metallic Impurities in 20% Ammonium Hydroxide by 7700s/7900 ICP-MS

Accurate Sizing and Precise Counting of 10 nm Gold Nanoparticles using the Enhanced Sensitivity of the NexION 2000 ICP-MS

Determination of trace elements in ultrapure semiconductor grade sulfuric acid using the Agilent 8900 ICP-QQQ in MS/MS mode

Elemental analysis of river sediment using the Agilent 4200 MP-AES

Analysis of domestic sludge using the Agilent 4200 MP-AES

High-Throughput Semiquantitative Screening of Ambient Air Samples by ORS-ICP-MS and Integrated Sample Introduction System (ISIS) Application

The Characterization of Nanoparticle Element Oxide Slurries Used in Chemical-Mechanical Planarization by Single Particle ICP-MS

Determination of major, minor and trace elements in rice fl our using the 4200 Microwave Plasma- Atomic Emission Spectrometer (MP-AES) Authors

Trace elemental analysis of distilled alcoholic beverages using the Agilent 7700x ICP-MS with octopole collision/ reaction cell

Ultra trace measurement of potassium and other elements in ultrapure water using the Agilent 8800 ICP-QQQ in cool plasma reaction cell mode

Accurate Analysis of Trace Mercury in Cosmetics using the Agilent 8900 ICP-QQQ

Macrolides in Honey Using Agilent Bond Elut Plexa SPE, Poroshell 120, and LC/MS/MS

Fast Analysis of Water Samples Comparing Axially-and Radially- Viewed CCD Simultaneous ICP-OES

Analysis of Arsenic, Selenium and Antimony in Seawater by Continuous-Flow Hydride ICP-MS with ISIS

Determination of Chromium in Gelatin Capsules using an Agilent 7700x ICP-MS

Application. Determination of Trace Metal Impurities in Semiconductor-Grade Hydrofluoric Acid. Authors. Introduction. Abstract.

Determination of challenging elements in ultrapure semiconductor grade sulfuric acid by Triple Quadrupole ICP-MS

Application note. Trace level analysis of sulfur, phosphorus, silicon and chlorine in NMP using the Agilent 8800 Triple Quadrupole ICP-MS

Determination of Pb, Cd, Cr and Ni in Grains Based on Four Chinese National Methods via Zeeman GFAAS

Formation of iron oxide nanoparticles for the photooxidation of water: Alteration of finite size effects from ferrihydrite to hematite

Ultra-fast determination of base metals in geochemical samples using the 5100 SVDV ICP-OES

Direct Analysis of Trace Metal Impurities in High Purity Nitric Acid Using ICP-QQQ

Application note. Determination of exchangeable cations in soil extracts using the Agilent 4100 Microwave Plasma-Atomic Emission Spectrometer

High Throughput Water Analysis using Agilent 7900 ICP-MS coupled with ESI prepfast

Accurate Determination of TiO 2 Nanoparticles in Complex Matrices using the Agilent 8900 ICP-QQQ

ICP-OES Application Note Number 35

Techniques for the Analysis of Organic Chemicals by Inductively Coupled Plasma Mass Spectrometry (ICP-MS)

The Agilent 7700x ICP-MS Advantage for Drinking Water Analysis

Insights Into the Nanoworld Analysis of Nanoparticles with ICP-MS

Comparing Collision/Reaction Cell Modes for the Measurement of Interfered Analytes in Complex Matrices using the Agilent 7700 Series ICP-MS

Analysis of NIST Gold Nanoparticles Reference Materials Using the NexION 300 ICP-MS in Single Particle Mode

Rapid Analysis of High-Matrix Environmental Samples Using the Agilent 7500cx ICP-MS. Application. Author. Abstract. Introduction.

Analysis of Ethanol and Isotopomers by 240 Quadrupole Ion Trap GC/MS

High Sensitivity HPLC Analysis of Perchlorate in Tap Water Using an Agilent 6460 Triple Quadrupole LC/MS System

Direct Analysis of Photoresist Using Inductively Coupled Plasma Mass Spectrometry (ICP-MS) Application

Analysis of Trace Metal Impurities in High Purity Hydrochloric Acid Using ICP-QQQ

Imaging gold nanoparticles in mouse liver by laser ablation inductively coupled plasma mass spectrometry

Quantitative analysis of high purity metals using laser ablation coupled to an Agilent 7900 ICP-MS

Study of Nanoparticles in a Few Rivers in North East Italy using SP-ICP-MS

Accurate Quantification of Cadmium, Chromium, Mercury and Lead in Plastics for RoHS Compliance using the Agilent 7500ce ICP-MS

ICP-3000 Inductively Coupled Plasma Optical Emission Spectrometer

PS1-10 COMPARISON OF SIZE-DETERMINING TECHNIQUES FOR NANOPARTICLES IN SUSPENSION: APPLICATION TO Ag NPs.

Simple, reliable analysis of high matrix samples according to US EPA Method 6020A using the Agilent 7700x/7800 ICP-MS

Accurate Mass Measurement for Intact Proteins using ESI-oa-TOF. Application Note. Donghui Yi and Christine Miller Agilent Technologies

Environmental Consequences of Nanotechnologies

Sensitive Detection of 2-MIB and Geosmin in Drinking Water

Analysis of Biomarkers in Crude Oil Using the Agilent 7200 GC/Q-TOF

Thermo Scientific icap TQ ICP-MS: Typical limits of detection

The Investigation of Fertilizer Analyses Using Microwave Digestion and the Agilent 720-ES

Rapid Sample Assessment and Simplified Method Development with IntelliQuant

Aminoglycosides in Milk Using Agilent Bond Elut Plexa SPE, Agilent Poroshell 120, and LC/Tandem MS

Rapid Screening and Confirmation of Melamine Residues in Milk and Its Products by Liquid Chromatography Tandem Mass Spectrometry

Key Words Nanoparticles, spicp-ms, ICP-MS, Qtegra ISDS Software, AF4-ICP-MS

Simple and Reliable Soil Analysis using the Agilent 7800 ICP-MS with ISIS 3

Agilent Cary 630 FTIR sample interfaces combining high performance and versatility

Multi-Element Analysis of Cannabis using the Agilent 7800 ICP-MS

Overcoming Interferences with the Thermo Scientific icap 7000 Plus Series ICP-OES

Single Particle Inductively Coupled Plasma Mass Spectrometry: A Powerful Tool for Nanoanalysis

Determination of Total Volatile Organic Compounds in Indoor Air Using Agilent 7667A mini TD and 7820A GC

Determination of Hormones in Drinking Water by LC/MS/MS Using an Agilent InfinityLab Poroshell HPH Column (EPA 539)

Application Note. Authors. Abstract. Introduction. Environmental

Analysis of Cerium Dioxide Nanoparticles in Soil Using Single Particle ICP-MS

Speciation of Bromine Compounds in Ozonated Drinking Water using Ion Chromatography and Inductively Coupled Plasma Mass Spectrometry

Agilent 8900 Triple Quadrupole ICP-MS

Application note. Accurate determination of sulfur in biodiesel using Isotope Dilution-Triple Quadrupole ICP-MS (ID-ICP-QQQ) Petrochemical

This installment of Atomic Perspectives discusses. Single-Particle ICP-MS: A Key Analytical Technique for Characterizing Nanoparticles

Hands on mass spectrometry: ICP-MS analysis of enriched 82 Se samples for the LUCIFER experiment

Determination of Phosphorus and Sulfur with Dynamic Reaction Cell ICP-MS

Semiquantitative Screening of Pharmaceutical Antiviral Drugs using the Agilent 7500ce ICP-MS in Helium Collision Mode

Analysis of Stachydrine in Leonurus japonicus Using an Agilent ZORBAX RRHD HILIC Plus Column with LC/ELSD and LC/MS/MS

Analysis of Low-Calorie Sweeteners by Liquid Chromatography-Tandem Mass Spectrometry

ICP-OES DETERMINATION OF IRON. Introduction:

Determination of Impurities in Silica Wafers with the NexION 300S/350S ICP-MS

Nanoparticle Analysis: An Upcoming Challenge for Environmental Analysis

Accurate Mass Analysis of Hydraulic Fracturing Waters: Identification of Polyethylene Glycol Surfactants by LC/Q-TOF-MS

Following documents shall be used for reference on quantities, units, prefixes and other technical vocabulary in this document:

Rapid determination of five arsenic species in polished rice using HPLC-ICP-MS

Quantitative characterization of silica nanoparticles by asymmetric flow FFF MALS-ICP-QQQ using the Agilent 8800 ICP-QQQ

Determination of Chlorinated Acid Herbicides in Soil by LC/MS/MS Application Note

Rapid Screening and Analysis of Components in Nonalcoholic Drinks Application

Determination of Nanoparticle Sizeand Number Concentration using the npquant Evaluation Module for Qtegra ISDS. The world leader in serving science

Value of Eclipse Plus C18 and ph Selectivity to Analyze Amine-Containing Drugs

Rapid and precise calcium isotope ratio determinations using the Apex-ACM desolvating inlet system with sector-field ICP-MS in low resolution

On-line isotope dilution analysis with the 7700 Series ICP-MS: Analysis of trace elements in high matrix samples

Exceptional Selectivity of Agilent ZORBAX Eclipse Plus Phenyl-Hexyl Columns to Separate Estrogens

Automated determination of the uniformity of dosage in quinine sulfate tablets using a fiber optics autosampler

Analysis Repeatability of Trace and Major Elements in a Water Sample

Applications of ICP-MS for Trace Elemental Analysis in the Hydrocarbon Processing Industry

hydrideicp Hydride Generation System

Transcription:

Single particle analysis using the Agilent 7700x ICP-MS Application note Authors Materials Sébastien Sannac 1, Soheyl Tadjiki 2, Evelin Moldenhauer 3 1 Agilent Technologies, France 2 Postnova Analytics Inc., UT, USA 3 Postnova Analytics GmbH, Landsberg, Germany Introduction Nanoparticles (NPs) are defined as ultrafine particles with one dimension between 1 100 nm [1]. Because of their small size, they have a very large surface area relative to their weight, so they often react quite differently from a bulk solid or dissolved material of the same composition. For this reason they may offer novel and interesting properties for a broad range of applications. Current and potential applications for NPs range from food additives, cosmetics and pharmaceuticals, to biocidal packaging, fuel cell technology and electronics. But while their use is constantly increasing, questions and concerns have been raised about their safety and their health impact. For this reason, there is an urgent need to develop analytical methods that are suitable for the particular evaluation of NPs. These methods need to be appropriate to the specific properties of nanoparticles,

and so should allow not only the determination of the NPs mass concentration, but also the evaluation of their size and size distribution. An interesting approach for the characterization of NPs has been developed by Degueldre et al. [2] based on elemental determination using Inductively Coupled Plasma Mass Spectrometry (ICP-MS). If samples containing NPs are introduced at a low flow rate and the number of particles in the solution is sufficiently low, analysis using ICP-MS in time resolved mode makes it possible to collect the intensity for a single particle as it is vaporized and atomized in the plasma. Then, each measured data point can be correlated to the size and mass fraction of a unique NP. This method of NP characterization is called Single Particle ICP-MS (SP-ICP-MS) analysis. The key feature of this analysis lies in the capacity of the ICP-MS to distinguish the data collected for each individual NP. For this reason, care must be applied in the sample dilution (particle number in solution) and in the selection of the integration time [3 5]. For a given content of NPs in the sample following its dilution, the integration time of the ICP-MS should be: Long enough to collect the entire signal from one NP and avoid the partial measurement of the particle, which would lead to an underestimation of its size. This point is also important in ensuring that the NP signal can be accurately discriminated from the background signal [4], Short enough to avoid the measurement of two NPs in a single integration period, which would lead to an overestimate of the size of the NPs, and an underestimate of the particle number [3, 5]. In the present work the analysis of various NPs has been carried out using the Agilent 7700x in SP-ICP-MS mode. Initially, the analysis of gold standards from NIST was used to evaluate the method for the detection of NPs sizes. Then, the method was applied to the characterization of samples containing gold and silver NPs. Experimental Instrumentation Measurements of NPs were performed using the Agilent 7700x ICP-MS. The samples were introduced directly into the ICP-MS system using the standard peristaltic pump with Tygon pump tubing (internal diameter of 1.02 mm), and ASX-520 autosampler. Analyses were performed in time resolved analysis (TRA) mode using an integration time of 3 ms for all measurements. While the integration times used in the literature vary, they are typically around 5 ms, and a maximum integration time of 10 ms is recommended [3 6] to avoid the double-counting mentioned previously. A rinse solution containing 1% nitric acid was used to ensure sample washout between each analysis. The general settings of the 7700x system are detailed in Table 1. Table 1. General settings of the 7700x ICP-MS Parameter Value RF power 1550 W Carrier gas 1.05 L/min Spray chamber temperature 2 C Nebulizer pump 0.1 rps Sample depth 8.0 mm Integration time 3 ms Acquisition time 60 s Mass monitored 107 Ag or 197 Au 2

Data analysis Details of approaches used for data processing and interpretation for SP-ICP-MS analysis can be found in the literature [3 6]. In the present work, a dedicated spread sheet developed by the National Institute of Food Safety in the Netherlands (RIKILT) was used for data conversion. Briefly, the custom spreadsheet uses the distribution plot of the signal intensities to allow the NP signals to be discriminated from the background (due to instrument noise and the signal from the dissolved component of the element in solution). The sensitivity of the ICP-MS (cps per µg/l) for the element of interest can be calibrated using conventional (non- NP) measurement of a standard solution, and so the signal peaks from the NPs can then be converted into the mass concentration of the element measured. The density of the material/element of interest is then entered into the spreadsheet, allowing the volume of each NP to be calculated. Based on the assumption that the NPs are spherical, the cube root of the NP volume can then be used to calculate each NP s diameter, allowing a size distribution plot to be generated, from which the median NP size is calculated. For the accurate conversion from intensities to particle sizes, the nebulization efficiency of the ICP-MS must be established, as well as the sensitivity for the target element. A sequence of analysis for samples containing NPs will therefore include at least the measurement of: A reference material with known NP particle size (for the evaluation of the nebulization efficiency) An ionic (dissolved) solution made from the same material as the unknown NP (for the determination of the ICP-MS sensitivity) The unknown sample(s) Ultimately, the SP-ICP-MS analysis and custom spreadsheet calculations are able to determine the number of particles present in the sample, their size distribution, the median size of the NPs population and the mass concentration for the element that the NP is composed of. Sample preparation Gold nanoparticle reference materials (RMs) NIST 8012 and NIST 8013, with reference values of 30 and 60 nm respectively, were purchased from NIST (Gaithersburg, MD, USA). Unknown gold or silver NP samples with different sizes were provided by different NP producers. The nanoparticle samples were diluted with water using polypropylene vials. Sample dilution was performed on the day of the analysis in order to avoid sample degradation. Before dilution of the samples and prior to their analysis, all solutions were placed in an ultrasonic bath for 15 min to ensure that the samples were fully homogenized. The gold NP standard at 60 nm (NIST 8013) was diluted to 5 ng/l Au concentration, for the evaluation of nebulization efficiency. Ionic solutions of gold and silver were diluted to 1 µg/l for the evaluation of the system sensitivity for each element. Each NP sample was diluted to ensure the measurement of between 200 2000 particle events per minute by SP-ICP-MS. This point is important to correctly measure the full signal from only one nanoparticle within each TRA integration. For this application, using the typical sample flow rate of the 7700x ICP-MS, the above particle number per minute correlates to approximately 10 7 particles per liter, which equates to an elemental concentration of between 5 500 ng/l, depending on the size and composition of the NPs. 3

Results and discussion Analysis of gold nanoparticles In order to evaluate the suitability of the ICP-MS method, a preliminary analysis of the reference NPs was performed. The gold NP standard (NIST 8012), which has a reference diameter of around 30 nm, was used for this purpose. A typical TRA acquisition for single NP measurement on the 7700x ICP-MS is shown in Figure 1. From this raw data, the background signal was eliminated by the custom spreadsheet, and the remaining intensities were converted into particle size to give the distribution pattern shown in Figure 2. From this size distribution plot, the median size was calculated to be 26.9 nm. This measured size is in good agreement with the reference value shown on the investigation report, which is 24.9 28.4 nm, depending upon the technique used for the measurement. The three replicate analyses of this sample gave a relative standard deviation of 0.5%, demonstrating the good repeatability of the 7700x SP-ICP-MS method. The particle number in the diluted sample was estimated at 1.6 x 10 7 particles/l and the mass concentration for Au was 3.2 ng/l. It should be noted that the data in Figure 2 show that no NPs were detected at a higher size range than the expected group in the 30 nm region. In particular around the 38 nm region where the signal should appear if a particle containing a cluster of two NPs was measured, the number of events measured is less than 2% of the total number of NPs detected. This observation suggests that the sample preparation approach was successful in ensuring that the measured NPs were distributed homogeneously, and were not present as an agglomeration of particles in the diluted sample. The absence of a significant number of particle events at a size greater than 30 nm also confirms that the chosen acquisition parameters did not lead to the measurement of more than one NP in each TRA integration period. Therefore, the integration time selected in the method was suitable for the discrete analysis of each individual NP introduced in the system. For a better evaluation of the developed method and to demonstrate that the method is able to discriminate NPs of a larger size, a mixture of gold NPs at 30 nm (NIST 8012) and 60 nm (NIST 8013) was also analyzed. 100000 90000 80000 70000 60000 Intensities 50000 40000 30000 20000 10000 0 0.014 3.217 6.42 9.623 12.826 16.029 19.232 22.435 25.638 28.841 Time (s) Figure 1. Typical TRA measurement of Single NPs. Example of the measurement of 30 nm gold NP standard (NIST 8012). 4

The result of this analysis is displayed in Figure 3. As can be seen, the method was clearly able to identify the presence of the two different NP sizes, with no overlap between the two different populations. The method has therefore been shown to have sufficient resolution to detect and discriminate between mixtures of different NP sizes within a single sample. Following the analysis of the NIST NP RMs, the remaining gold nanoparticle samples were measured as unknowns. Au NPs with a nominal particle size of 40 and 15 nm were analyzed as separate samples, and 100 90 the median particle size was found to be 38 and 16 nm respectively. The results for the characterization of those samples can be seen in Table 2. Table 2. Results for the analysis of unknown gold NPs Theoretical size 40 nm 15 nm Experimental size 38 nm 16 nm Particles number 5.5 x 10 7 particles/l 6.4 x 10 6 particles/l Element concentration 3.7 ng/l 0.3 ng/l Normalized frequency Normalized frequency 80 70 60 50 40 30 20 10 0 0 20 40 60 80 100 120 140 160 180 Particle size (nm) Figure 2. Particle size distribution for a 30 nm gold NP standard (NIST 8012) 100 90 80 70 60 50 40 30 20 10 0 0 20 40 60 80 100 120 140 160 180 Particle size (nm) Figure 3. Particle size distribution for a mixture of 30 nm and 60 nm gold NP standards (NIST 8012 and 8013) 5

Analysis of silver nanoparticles After the development of the gold nanoparticles method, the same procedure was applied to the analysis of silver NPs. A sample with indicative particle size of 20 nm was analyzed. The analysis of the 20 nm NPs led to a median size of about 18 nm, in good accordance with the indicative value (Figure 4). The number of particles was found to be 1.1 x 10 7 particles/l and the silver concentration was calculated to be 0.4 ng/l. However, the detection of this NP size was near the limit of the method, as the signal distribution for the NPs was close to the background signal measured by the ICP-MS. Conclusions The present work illustrates the suitability of the Agilent 7700x ICP-MS for the analysis of single nanoparticles. The method has been successfully applied to the analysis of gold and silver NPs with sizes ranging from 15 60 nm. The SP-ICP-MS method provided the size distribution, median size, number of particles and the elemental concentration of a given NP sample. Additional work may be required to fully validate the SP-ICP-MS measurement and data analysis approach, in particular to validate the calculations used when converting the measured intensities into NP sizes. To complement the results obtained by the SP-ICP-MS analysis, additional approaches should be used, such as Scanning Electron Microscopy (SEM) or the coupling of Field Flow Fractionation (FFF) devices with ICP-MS. 100 90 80 Normalized frequency 70 60 50 40 30 20 10 0 0 20 40 60 80 100 120 140 160 180 Particle size (nm) Figure 4. Particle size distribution for unknown silver NPs with indicative size of 20 nm 6

The next challenges for SP-ICP-MS analysis will be to apply the method to real samples which include a matrix that could create interferences, and to use the method for the measurement of nanoparticles containing elements such as titanium, iron or silicon, which are more challenging for ICP-MS due to the potential for spectral interferences. Acknowledgements We acknowledge the contribution of RIKILT, who provided the Microsoft Excel worksheet that was used in the present work to convert the raw SP-ICP-MS analysis data into NPs sizes. References 1. ISO TS 80004-1:2010: Nanotechnologies -- Vocabulary -- Part 1: Core terms 2. Degueldre S., Favarger P.-Y., Bitea C., (2004) Analytical Chimicta Acta, 518: 137-142 3. Laborda F., Jiménez-Lamana J., Bolea E., Castillo J.R., (2011) Journal of Analytical Atomic Spectrometry, 26: 1362-1371. 4. Tuoriniemi J., Cornelis G., Hassellöv M., (2012) Analytical Chemistry, 84: 3965-3972. 5. Mitrano D., Barber A., Bednar A., Westerhoff P., Higgins C., Ranville J., (2012) Journal of Analytical Atomic Spectrometry, 27: 1131-1142. 6. Pace H., Rogers J., Jarolimek C., Coleman V., Higgins C., Ranville J., (2011) Analytical Chemistry, 83: 9361-9369. 7

www.agilent.com/chem Agilent shall not be liable for errors contained herein or for incidental or consequential damages in connection with the furnishing, performance or use of this material. Information, descriptions, and specifications in this publication are subject to change without notice. Agilent Technologies, Inc. 2013 Published August 22, 2013 Publication number: 5991-2929EN