Claudia
Cascio
*a,
Otmar
Geiss
b,
Fabio
Franchini
a,
Isaac
Ojea-Jimenez
a,
François
Rossi
a,
Douglas
Gilliland
a and
Luigi
Calzolai
*a
aNanoBioSciences Unit, Institute for Health and Consumer Protection, European Commission-DG Joint Research Centre, Via Enrico Fermi 2749, Ispra, Italy. E-mail: claudia.cascio@jrc.ec.europa.au; luigi.calzolai@gmail.com; Tel: +39 0332 78 6561
bChemical Assessment and Testing Unit, Institute for Health and Consumer Protection, European Commission-DG Joint Research Centre Commission, Via Enrico Fermi 2749, Ispra, Italy
First published on 6th January 2015
In 2011 the European Commission published its recommendation for a definition for the term nanomaterial which requires the materials to be characterized in terms of the number size distribution of their constituent particles. More recently, the definition has begun to be applied to the labelling of food and cosmetic products where any components present in the form of engineered nanomaterials must now be clearly indicated in the list of ingredients. The implementation of this definition requires that methods be developed and validated to accurately size particles with at least one external dimension in the range of 1–100 nm, and to quantify them on a ‘number-based’ particle size distribution. An in-house developed method based on Asymmetric Flow Field Flow Fractionation-Inductively Coupled Plasma Mass Spectrometry (AF4-ICP-MS) for the simultaneous detection and quantification of citrate-stabilised silver nanoparticles (AgNPs) in water, has been applied to real-world liquid antimicrobial consumer products based on colloidal silver. This transfer of the method from ideal model systems to real products was assessed in light of other techniques including Centrifugal Liquid Sedimentation (CLS), Dynamic Light Scattering (DLS) and Transmission Electron Microscopy (TEM). Five out of six analysed products were found to contain AgNPs in the nano-range by means of a number of techniques including AF4-ICP-MS. Comparative analysis shows that CLS has sufficient size resolution to size AgNPs in the consumer products while DLS was unsuccessful probably due to sample polydispersivity. Despite the silver nanoparticles having unknown surface properties and stabilisation agents which could have influenced the sizing with AF4, a relatively good agreement between TEM and AF4-ICP-MS was observed. The AF4-ICP-MS data could be converted from mass-based to number-based distributions; this transformation, despite the possibility of experimental artefacts being mathematically amplified, has shown promising results.
Currently there is no single analytical method or instrument able to address the requirements of the definition but a variety of methods exist which, in combination, offer the possibility of tackle this problem.5,6
It is well recognised that among nanomaterials, silver nanoparticles (AgNPs) are the largest and fastest growing category in use in consumer products. In particular, their powerful antimicrobial properties7 and relatively low cost have led to silver nanoparticles being widely used in a number of applications including food contact materials,8 cosmetics, wall paints, textiles,9 laundry detergents, biocide sprays and medical devices.10 Over 430 consumer products are currently reported to be on the market11 with this number being expected to increase significantly in the coming years. Recently an Inventory of Nanotechnology applications in the agricultural, feed and food sector12 was published showing that silver (along with nano-encapsulates and titanium dioxide) is among the most exploited nano-technological materials and that food additives and food contact materials are the most common of the current applications.
From a toxicological point of view it is believed that the antibacterial properties13 of silver nano-particles are mainly due to the release of silver ions from AgNPs, with evidence of a size dependent in vitro AgNP toxicity associated with generation of reactive oxygen species, loss of mitochondrial activity and DNA damage.14–16 However there are still a number of critical points to be clarified, including possible in vivo transformation, accumulation and interaction with enzymes and biomolecules, before a definite conclusion about whether or not AgNPs are hazardous to humans can be established.17 In this scenario the development of methods for the simultaneous detection/quantification of AgNP from ionic and soluble species is crucial.
Among the techniques applicable to the detection and characterization of AgNPs in complex matrices, the use of Asymmetric Flow Field Flow Fractionation18 (AF4) coupled to Inductively Coupled Plasma-Mass Spectrometry (ICP-MS) appears extremely promising and applicable to a number of sample types including cell culture media19 and chicken meat.20 This approach combines the ability of AF4 to size-fractionate particles in the nano-range with the high sensitivity and element specificity of the ICP-MS, thus providing an ideal tool for the simultaneous detection and quantification of nanoparticles. Furthermore, being a technique for the analysis of liquid samples, AF4-ICP-MS allows the study of NP size distribution directly in their native dispersions, avoiding possible artefacts deriving from sample preparation and drying as it might happen in electron-microscopy analysis.4 Finally, AF4 is able to isolate AgNP from the ionic/soluble species, providing an appealing tool for ionic/particulate physico-chemical speciation. Single-particle ICP-MS and particle tracking analysis (PTA) are two techniques that can potentially provide the particle size distribution of silver nanoparticles. Both techniques have the advantage to count directly the number of particles, but have a lower limit of size detection of around 20 nm for AgNPs.21 In addition, at the moment, they are somewhat less robust than the AF4-ICP-MS combination and for PTA the measurements are highly operator-dependent.22
One of the disadvantages of AF4-ICP-MS is that method development can be time consuming leading to undesirable additional costs for testing laboratories.23 In order to reduce FFF method development time, in this work we applied a single AF4-ICP-MS method that has been previously optimised for citrate-stabilised AgNPs in the 10–110 nm range24 to a collection of commercial antimicrobial AgNPs samples. Thus, in contrast to other similar works published on the topic,25 our objective was not to adapt the AF4-ICP-MS method to individual products but rather to evaluate the results obtained from the straightforward application of a single standardized method to a range of real life samples. In doing this the performance of the AF4-ICP-MS method was compared to other sizing techniques such as Centrifugal Liquid Sedimentation (CLS), Dynamic Light Scattering (DLS) and Transmission Electron Microscopy (TEM). The data obtained was then used to verify whether or not the tested commercial samples contained nanomaterials according to the EC definition.
Nitric acid used was 67–69% ultrapure for trace analysis (CARLO ERBA Reagents S.r.l., Italy); silver and rhodium ICP-MS standards, at a concentration of 1000 mg L−1 in 2% nitric acid were purchased from Absolute Standards (Absolute Standards INC, Hamden, USA); the ultrapure water used throughout the experiments was supplied from a Millipore Advantage System (Merck Millipore, © Merck KGaA, Darmstadt, Germany). Sucrose (puriss.) used to create the liquid density gradient in the CLS was purchased from Sigma Aldrich (Sigma-Aldrich Corp., St. Louis, USA); the AF4 eluent was ultrapure water adjusted to pH 9.2 with 0.1 mM NaOH-solution and was freshly prepared every day.
Product | Colour | Declared silver form | Declared concentration [mg L−1] | Measured total silver& [mg L−1] |
---|---|---|---|---|
A | Pale yellow | Colloidal/ionic | 15 | 11.63 ± 0.09 |
B | Yellow | — | 10 | 9.3 ± 0.3 |
C | Yellow | — | 20 | 29.3 ± 0.1 |
D | No colour | Colloidal/ionic | 20 | 2.19 ± 0.07 |
E | Yellow | Colloidal | 20 | 25.6 ± 0.3 |
F | Yellow | Colloidal | 10 | 9.50 ± 0.03 |
Total silver in the consumer products was determined by ICP-MS following dilution in 2% nitric acid. A two-step dilution strategy (average total dilution factor 500×) was used in which pure nitric acid was firstly allowed to react with the consumer products for 3 hours at room temperature before dilution. All samples, quality controls and standards were prepared gravimetrically on a 4 digit scale. All samples and ionic silver spikes were prepared and analysed in triplicate. After preparation samples were promptly analysed for total silver concentration by ICP-MS.
Parameter | Details |
---|---|
AF4 settings | |
Permeation membrane | 10 kDa regenerated cellulose |
Injection-loop volume (μL) | 50 |
Wavelength (UV-VIS detector) | 420 nm |
Eluent | basified ultrapure water |
pH | 9.2 |
Focusing time | 5 minutes |
Applied cross flow (mL min−1) | From 1 to 0.1 |
Gradient type | Linear decay in 35 minutes |
ICP-MS settings | |
RF-power (W) | 1550 |
Reflected-power (V) | 12.2 |
Plasma temperature (K) | 6500–8000 |
Nebulizer | MicroMist (quartz) |
Spray chamber | Scott (quartz) |
Scan mode and resolution | Time resolved analysis |
Integration time (s) | 0.3 (Ag), 0.120 (Rh) |
Monitored masses | 107, 109, 103 |
Centrifugal Liquid Sedimentation (CLS) revealed the presence of nanoparticles in 5 out of 6 products analysed (Fig. 2C and Table 3). CLS results confirmed the presence and relative quantities of the particle indicted by the UV-VIS analysis, while sample D did not show any detectable particles. Products B, C, F and E and A were all found to contain nanoparticles with 100% of the particle size distribution (in weight) below 100 nm. In particular, Products B, C, F and E showed very broad peaks centred below 15 nm, while Product A showed a small peak centred at 17.4 nm.
Method | Product A | Product B | Product C | Product D | Product E | Product F |
---|---|---|---|---|---|---|
a Peak maximum provided by CLS software from particle size distribution in weight; (σ calculated from the peak half height width provided by CLS software dividing by 2.354). b Z average calculated from DLS software ±Z average × √PDI. c Distribution peak centre. d Average ± standard deviation. | ||||||
CLSa | 17.4 (1.5) | 13.3 (7.3) | 12.1 (7.2) | — | 12.6 (6.8) | 13.6 (7.1) |
TEMd | P1 15.1 ± 4.5 | 12.4 ± 5.7 | 11.9 ± 5.1 | — | 11.6 ± 4.4 | 13.6 ± 5.6 |
P2 42.2 ± 11.6 | ||||||
AF4-ICP-MSc (mass) | P1 33.8 | 16 | 16 | — | 18.5 | 17.4 |
P2 47.3 | ||||||
AF4-ICP-MSc (number) | P1 31.4 | 10.9 | 9 | — | 14.5 | 11.5 |
P2 48.9 | ||||||
DLS (Z-average)b | 224.7 ± 134.8 | 66.9 ± 25 | 53 ± 40.7 | 155.3 ± 80.7 | 36.8 ± 29.2 | 66.6 ± 43.2 |
DLS (PdI) | 0.36 | 0.14 | 0.59 | 0.27 | 0.63 | 0.42 |
Z-potential | −41.4 | −36.8 | −54 | — | −49.8 | −44.3 |
Batch DLS analysis was performed on undiluted consumer products (Table 3 and Fig. S.1 in ESI†). In the majority of cases, the polydispersivity index (PdI) of the products was quite large indicating low monodispersivity and/or possible matrix effects. For Product A, duplicate analysis on batch DLS produced poorly reproducible results and in one of the two measurements a bimodal distribution was detected (Fig. S.1.A of ESI†). All the detected Z-averages are greater than diameters generated by CLS probably due to a small number of larger particles or aggregates which, due to the highly non-linear variation of scattering intensity with particle size which, can introduce errors in DLS biasing the calculated mean size towards larger values.27
In contrast with DLS, CLS shows a greater ability to deal with heterogeneous dispersions, due to size fractionation before particle detection. CLS has proven to be considerably more suitable than DLS for the characterisation of multi-modal AgNP suspensions, and in particular to resolve bimodal mixtures of AgNPs.28 Nonetheless CLS, being a centrifugation based technique, depends on knowing a value of particle density which is normally assumed to correspond to the bulk metal one (10.49 g cm−3). While such an approximation may be valid for uncoated particles, it may create a systematic error with polymer or protein coated particles, and this effect might be especially significant on very small particles.29 Since it was not possible to assess the nature of any capping agent, coating or stabiliser in this study, some error related to the assumed particle density might ultimately affect the sizing by CLS.
TEM observations of the six products confirmed the presence of quasi-spherical nanoparticles in all samples with the exception of Product D (Fig. 3), which did not show any sign of nano- or macro-particles (Product D image not reported). Image analysis of Products B, C, E and F produced narrow size distributions with mean size values between 11–14 nm (Fig. 3, Table 3). However, Product A showed a more polydisperse distribution of NPs, which might be approximated as two populations: 1st with a mean size of 15 nm and a 2nd of 42.6 nm. However, this bimodal trend was not detected by CLS. For sample C, TEM observations showed a tail up to 30 nm, but the mean size is 11.9 nm. Indeed Product C showed a tendency to change colour from yellow to blue/grey when small aliquots were stored (1 week) in the fridge without rigorous exclusion of oxygen. This was confirmed as a shift of the LSPR peak in the UV-VIS absorbance spectrum (ESI†) which is assumed to be an indication of possible aggregation and/or surface oxidation.26,30
For mass calibration a method based on pre-channel injection was adopted22 in which accurately known quantities of three size AgNPs (nominal diameters 20 nm, 60 nm, 100 nm) on three concentration levels (0, 25 and 60 ng of total silver) were injected using a 50 μL loop before applying the standard elution profile. Three different calibration curves were built for each of three particle sizes respectively. This particular approach has both advantages and disadvantages – on one hand it has been previously demonstrated to be effective in compensating for incomplete particle channel recovery compared to ionic silver post-channel calibration24 but is hindered by the lack of AgNPs certified standards for size and concentration. To overcome this problem it was necessary to in-house determine the concentration of silver particles in the stock solutions.24
The ICP-MS on-line detector showed a Limit of Detection (LoD) (average blank + 3SD blank/slope) between 0.170–0.340 μg L−1 and a Limit of Quantification (LoQ) (average blank + 10SD blank/slope) in the range 0.566–1.133 μg L−1 for different particle sizes in line with previous results reported in literature.25
Fractograms obtained with both the UV-VIS detector and ICP-MS are shown in Fig. 4 which shows an example of the AgNPs mass calibration mixture together with data relative to the five consumer products. The five consumer products which showed a detectable amount of silver gave clear signals detectable both on UV-VIS and ICP-MS detectors with main peaks being well separated from the void peak. For the purpose of clarity, the UV-VIS detector signal collected at 420 nm (black-left axes) and ICP-MS (coloured lines, right axes) have been aligned by the void peak. After a preliminary run for each sample, dilution factors were chosen to avoid to overload the detector and to ensure quantification within the calibration curve. Exact dilution factors in ultrapure water before injection were the following: Product A: none; Product B: 10.97; Product C: 20.1; Product E: 16.7, Product F: 19.7.
Channel recovery for real consumer products was evaluated by injecting samples with and without cross-flow and comparing the different peak areas obtained on the UV-VIS. Recovery was calculated as:
%Recovery = 100 × peak area EL/peak area NC |
Channel recoveries were the following: 70% for Product A, 88% for Product B, 94% for Product C, 80% for Product F, 96% for E, and 85% for 20 nm AgNPs here used as standard. In our previous work the estimation of the size-related recovery was performed systematically on five replicates demonstrating the absence of significant difference for citrate-coated particles of 10, 20, 40 and 60 nm.24 In this context, considering the insignificant changes in detected particle size in the consumer products such a variation in recovery might be due more to surface chemistry and consequentially to membrane interaction.
To convert count ratio into concentration, the slope of the 20 nm AgNP calibration curve (count ratio versus area) was used. A curve fitting was done using OriginPro.7.5 and the ‘Gauss mod’ function (an exponentially modified Gaussian peak function for use in Chromatography) (details in Table S.3 of ESI†). Peak areas were used for quantification of the particulate silver (details in paragraph S.2 of ESI†) taking into account channel recovery rate and compared to total silver content determined by batch ICP-MS (Fig. 1, Table S.4 of ESI†). From these estimates, Product A was found to contain less than 2% of total silver as particulate silver; on the contrary Product C was found to contain over 85% of particulate silver. Fig. 1 (red bars) shows the AgNP content in the consumer products obtained by this approach; a similar trend was observed from CLS (peak height) and UV-VIS analysis with Product A being the one with the lowest particle concentrations and Product C being the highest, and with Product B and F having an intermediate content of particulate silver. For Product E, a qualitative analysis of UV-VIS and CLS data suggests a content of silver nanoparticles comparable to Product C (Fig. 2A and C), while the data from AF4-ICP-MS shows that it contains around 50% less silver NP than Product C (Table S.4†). The reason for this underestimation is unclear.
(i) The relationship between particle size and elution time when using the ICP-MS detector was determined as follows: a size vs. elution time calibration was performed daily with a mixture of citrate-stabilised AgNPs of known size; previous findings during method development showed elution times to be reproducible with a relative standard deviation generally below 1.5% on 14 replicate measurements performed on both intra-day and inter-day basis for different particle sizes.24 To do this a suspension containing 10 nm, 20 nm, 40 nm, 60 nm and 100 nm citrate stabilised AgNPs was run daily as a channel calibration mixture as in Fig. S.2.A of ESI.† The good reproducibility of the elution time–particle size relationship measured using the ICP-MS detector permitted it to be used for sizing silver nanoparticles in consumer products. An example of applied equation is
Size = 0.027(elution time)2.38 |
(ii) The correspondence between counts and mass of silver in each ICP-MS sampling time was calculated from the integrated elution peak areas obtained from injections of known masses of 20 nm AgNPs.
(iii) By applying the correspondence determined in (ii) to the ICP-MS detector signal for unknown samples the number of counts accumulated in each sampling period was converted in a mass of silver in that time interval.
(iv) Since the mean particle size at each data point in the eluting profile is known from step (i), the volume and theoretical weight of the individual particles at each time point can be calculated by assuming the density of bulk silver of 10.49 g cm−331 and spherical geometry.
(v) From the total mass of silver in each given time interval and the corresponding mass expected for each particle the total number of particles in a certain time sampling period can be calculated.
As a confirmation of the quality of this sizing approach a mixture of 20 nm, 60 nm and 100 nm citrate-stabilised AgNPs was sized, providing satisfactory results of 20.3 (5.4) nm, 59.4 (10.4) nm and 95.1 (15.4) nm for peak centre (FWHM) when a gauss function was fit on data in OriginPro 7.5. In terms of mass, the 20 nm 60 nm and 100 nm mixture was analysed in a 1:1:1 mass ratio (Fig. 5A); the experimental values were compared to the expected ones, based on the known injected mass (459.35, 463.01 and 444.9 μg L−1 for 20, 60 and 100 nm respectively) and the measured TEM diameters (19.6, 57.4 and 99.4 nm respectively). The measured relative mass-PSD of 33.1%, 31.2%, 32.3% compares well with the expected values of 33.6%, 33.9% and 32.5% for the 20, 60, and 100 nm AgNP (Fig. 5B).
The above described strategy allowed converting the mass-based PSD into the number-based PSD. Such analysis gave an experimental relative number PSD of 95.8%, 3.4% and 0.8% for the small, medium and large AgNP, respectively. Such distribution compares well with the predicted number-PSD of 95.6%, 3.7% and 0.7%.
The effect of conversion from mass to number of particles clearly produces a great enhancement of the relative contribution from 20 nm compared to the 100 nm that very well reflects the predicted mass and number ratio calculated (respectively grey and blue bars in Fig. 5B). In performing this operation it is important that the lower size cut-off point be correctly selected to avoid errors from inclusion of materials in the void-peak. Indeed if the cut-off is fixed too early, the void peak will be included in the calculation and erroneously considered as small particles. This effect has been studied in detail for the model sample AgNPs 20, 60, 100 nm (Fig. S.3 in ESI†): the smaller the cut-off the higher the risk that a part of the void peak be incorrectly considered to be small sized particles with D50 for number PSD ranging from 3 nm up to 19 nm when going from a cut off of 2 up to 10 nm. For most of the samples analysed in this study the cut-off is set at 8 nm.
It should be noted that although the mass to number transformation is relatively simple to achieve, it suffers from a number of limitations, either intrinsically related to the analytical method or related to data conversion. For the latter case, the fact that the generically named as ‘silver nanoparticles’ present in consumer products could include a number of different surface chemistries; for example, silver–chitosan–poly(ethylene glycol) nanoparticles,32 and silver/poly(lactic acid)33 have been reported for antibacterial applications. Such ‘silver nanoparticles’ might show an unpredictable behaviour during channel elution, such as repulsion or attraction to the membrane potentially leading to variations in retention time and/or recovery. To some extent, the suitability of an unknown particle type could be verified by measuring its Z-potential under standard elution conditions and comparing it with that found for the citrate-stabilize particles. If the measured Z-potential values are substantially higher of lower than for the size-calibrants, extreme care should be taken in using elution time to derive the particle size since it might produce an erroneous size determination based on retention time only. In the extreme case of positively charged particles our method would likely be ineffective due to the strong interactions with the negatively charged membrane at the working pH of 9.2.
In addition, any inaccuracies in the experimentally determined weight-size distribution are disproportionately magnified by the mathematical conversion to the desired number-size distribution. In particular, the smaller the particles the greater is the potential error in number. Finally, the conversion from mass to number assumes that the particles have spherical geometry and that their density corresponds to that of bulk silver.
Bearing in mind the possible limitations discussed above the raw data for the five consumer products was elaborated to obtain mass and number size distributions together with their associated cumulant curves (Fig. 6). For the consumer samples analysed here a size cut-off value of 8 nm was chosen. This size corresponds to an elution time of 10.5 min with the ICP-MS detector and thus well away from the void peak occurring at around 7 min. For one sample only (Product A), the cut-off had to be set at 18 nm due to a broad void peak. The 8 nm cut-off chosen for the AF4-ICP-MS analysis could skew the particle size distribution, especially with respect to that one measured by TEM that is able to measure particles smaller than 8 nm. In any case the centres of the number distributions obtained by AF4-ICP-MS and TEM (Table 3) are remarkably similar.
For Products B, C, E and F the number based particle size distribution gives sizes (as measured by the centre of the PSD distribution) that are smaller than the mass-based PSD (as expected). In general, the number-based PSD obtained from the AF4-ICP-MS analysis is closer to the values measured by electron microscopy (Table 3) then the mass-based ones. For example, Product B had a mass-based PSD peak maximum at 16 nm and a number-based PSD peak maximum at 10.9 nm that compares quite well with the electron microscopy based PSD average of 12.4 nm. The cumulant analysis is also a very useful way to report the PSD and it is probably more relevant for the EC definition of nanomaterials. The calculated values of D50m (50% of the particles in the mass-based PSD) and D50n (50% of particles in the number-based PSD) were (32.8 nm, 12.1 nm), (30.6 nm, 11.6 nm), (26.2 nm, 15.4 nm) and (37.5 nm, 12.9 nm) for Products B, C, E and F respectively. Product A represented a slightly more complex case due the presence of a bimodal distribution both in TEM (Fig. 3A) and in AF4-ICP-MS analysis (Fig. 6A). Although a discrepancy is present between sizes of the two populations obtained with the two techniques (33.8, 48.9 nm by AF4-ICP-MS and 15.1, 42.2 nm by TEM) it is remarkable that AF4-ICP-MS is able to detected two populations and their relative number-based PSD (Fig. 6A, red line) is coherent with that obtained by electron microscopy (Fig. 3A).
The mass and number-based PSD obtained by AF4-ICP-MS analysis indicates that all the five consumer products by AF4-ICP-MS analysis contain more than 50% of particles in the size range below 100 nm (Table 3 and Fig. 6). On this basis the AF4-ICP-MS analysis would have classified the five products analysed as being ‘nanomaterials’ under the terms of the EU definition.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c4ja00410h |
This journal is © The Royal Society of Chemistry 2015 |