We describe a procedure for the detection of chemical elements present in situ in human cells as well as their in vitro quantification. The method is well-suited to any cell type and is particularly useful for quantitative chemical analyses in single cells following in vitro metal oxide nanoparticles exposure.
Micro-analytical techniques based on chemical element imaging enable the localization and quantification of chemical composition at the cellular level. They offer new possibilities for the characterization of living systems and are particularly appropriate for detecting, localizing and quantifying the presence of metal oxide nanoparticles both in biological specimens and the environment. Indeed, these techniques all meet relevant requirements in terms of (i) sensitivity (from 1 up to 10 µg.g-1 of dry mass), (ii) micrometer range spatial resolution, and (iii) multi-element detection. Given these characteristics, microbeam chemical element imaging can powerfully complement routine imaging techniques such as optical and fluorescence microscopy. This protocol describes how to perform a nuclear microprobe analysis on cultured cells (U2OS) exposed to titanium dioxide nanoparticles. Cells must grow on and be exposed directly in a specially designed sample holder used on the optical microscope and in the nuclear microprobe analysis stages. Plunge-freeze cryogenic fixation of the samples preserves both the cellular organization and the chemical element distribution. Simultaneous nuclear microprobe analysis (scanning transmission ion microscopy, Rutherford backscattering spectrometry and particle induced X-ray emission) performed on the sample provides information about the cellular density, the local distribution of the chemical elements, as well as the cellular content of nanoparticles. There is a growing need for such analytical tools within biology, especially in the emerging context of Nanotoxicology and Nanomedicine for which our comprehension of the interactions between nanoparticles and biological samples must be deepened. In particular, as nuclear microprobe analysis does not require nanoparticles to be labelled, nanoparticle abundances are quantifiable down to the individual cell level in a cell population, independently of their surface state.
Cellular homeostasis is determined by the uptake control, assimilation, and intracellular localization of different trace elements (ions, metals, exogenous inorganic compounds). These components are frequently in the form of traces, but nevertheless may have a considerable impact in the system physiology. Thus, the study of cell biochemistry in both normal and pathological/stressed situations is a key-step towards an overall understanding of cellular metabolic mechanisms. Therefore, the development of imaging and analytical techniques enabling the investigation of intracellular chemical abundances, structural organization and their related metabolic functions becomes necessary. Very few methods are able to provide an in situ quantitative piece of information concerning the overall chemical nature of a given sample. Apart from methods analyzing samples in the bulk form, in situ analyses consider biological samples in their integrality without losing mass and structural information, thereby preserving their constituent chemicals (trace elements and ions) and proteins. Furthermore, as the nanosciences continue to develop, improved imaging and analytical methods for environmental monitoring at the cellular scale will be necessary to observe and quantify nano-object behaviors and interactions.1
Nanoparticles (NPs) have been defined as objects exhibiting at least one facial dimension in the range 1 and 100 nm.2 Due to their particular physicochemical properties, NPs are extensively used in industry. NPs are employed in bio-applications and in nanomedicine.3,4 Despite the numerous physicochemical characteristics of NPs, they may generate some risks of adverse effects on human health and environment. These risks can be induced by both prolonged and repetitive exposures at various concentration levels and this has not yet been clearly established.5,6,7,8 In particular, the fate of NPs inside cells and the associated cellular responses are, to date, not fully described. This is in part due to the scarcity of methods that allow the detection and quantification of internalized NPs in a single cell.9
The classical analytical tools used to estimate the cellular dose of nanoparticles are microscopies, mass spectrometry (MS), inductively coupled plasma MS (ICP-MS)10,11 and liquid chromatography MS (LC-MS), but they only provide useful information at the macroscopic scale. None of them can provide a precise evaluation of the subcellular NPs content nor the NPs distribution without the use of fractionation methods. A systematic assessment of the dose-response is thus impossible with these methods, as opposed to methods based on atomic spectroscopy such as nuclear microprobe analysis12,13, synchrotron X-ray fluorescence microscopy14, and Secondary Ion Mass Spectrometry (SIMS).15,16 These methods are particularly interesting as they complement observations made using fluorescence microscopy, especially when NPs cannot be labeled with fluorescent molecules and are thus studied in their native state. To some extent, even when NPs are grafted with fluorophores, (i) quantification remains difficult because the tagging level per NP is unknown and (ii) the chemical modification of the NP surface may modify its cellular distribution.
In this article, we focus on a method based on a combination of nuclear microprobe techniques aiming at imaging the morphology and elemental composition of biological specimens in major, minor, and trace concentrations.
Nuclear microprobe analysis proves to be particularly suitable for the measurement of trace chemical elements in biological tissues. Both the beam lateral resolution (0.3 to 1 µm) and sensitivity in chemical element detection (from 1 to 10 µg.g-1 dry mass) are well suited for studies at the cellular level. Nuclear microprobe techniques are based on particles detection (photons, electrons, ions) emitted after the ion beam (typically running at MeV energies) interacts with atoms present in the sample. Interactions occurring in cells are mainly: 1) excitation/ionization of atoms followed by an emission of photons after atoms return to their fundamental state; and 2) diffusion of incoming particles leading to change in their energy and direction. The measurement of emitted particle energy allowsthe identification of atoms involved in the interaction. To perform mapping of elements, the ion microbeam is repeatedly scanned over the sample surface, often over an area of about 100 by 100 µm2 containing several cells. Emitted particles are detected and their energy is recorded for each beam position. Sorting of particles according to the beam position, thus identifying the structure responsible for the emission of such particles is the aim of data treatment. Here, we precisely describe an approach based on fluorescence microscopy and nuclear microprobe analysis to detect as well as to quantify exogenous NPs at the cellular and sub-cellular scales, in order to investigate the consequences of NP interactions with living systems. We shall particularly focus on the opportunities offered by this method in terms of in situ quantification of titanium dioxide nanoparticles (TiO2 NPs) aggregates at the subcellular level.
1. Sample Holder Preparation
2. Growth of Cells in the Appropriate Sample Holder.
Caution: Protocol must be carried out in a biosafety laminar flow bench (Class II) to exclude contaminating micro-organisms. Handle antibiotics (e.g. penicillin, streptomycin) with gloves. Respect best practices when handling biological materials (Cell lines, genetically modified derived human cells).
Critical: The cell lines used should be checked to ensure that they are not infected with Mycoplasma.
3. Nanoparticles Preparation and Exposure
NOTE: Fluorescent dye-modified TiO2 NPs were designed, synthesized, and chemically modified with tetramethyl rhodamine isothiocyanate (TRITC).20,21 This surface modification allows nanoparticle detection, tracking and localization in situ and in cellulo in both living and fixed cells or in multicellular organisms.12,13,18
Caution: Nanomaterials and Nanoparticles must be handled with care. Avoid inhalation, ingestion or contact with skin. To prevent dissemination in air, nanoparticles are maintained in solution (ultrapure water).
4. Paraformaldehyde fixation and fluorescence microscopy.
5. "Plunge-Freezing" Fixation and Dehydration
6. Nuclear Microprobe Analysis
NOTE: Nuclear Microprobe Analysis was carried out at the microbeam line of AIFIRA (Applications Interdisciplinaires des Faisceaux d'Ions en Région Aquitaine) using the complementary ion beam analytical techniques Particle Induced X-ray Emission (µ-PIXE) and Scanning Transmission Ion Microscopy (µ-STIM). The facility is based on a 3.5 MV particle accelerator delivering light ion beams in the MeV energy range.22,23
Pause point: AIFIRA is an ion beam facility hosted by the University of Bordeaux that offers an access to national and international teams after scientific evaluation of the proposed experiment.
7. Data analysis
Cell culture and fluorescence imaging of fluorescently labeled TiO2 NPs
We designed a sample holder adapted for cell culture, cell handling as well as multimodal analysis. Specifically, it was important that the holder permitted routine optical microscopy as well as nuclear microprobe analysis and imaging. This sample holder is based on a 2-µm thick polycarbonate foil deposited on a PEEK frame. Cells are directly grown on polycarbonate, in sterile culture conditions for several days and then used for different experimental settings, such as NPs exposure.
The chemical surface modification with fluorophores (TRITC) allowed the detection of the TiO2 NPs as well as their in situ and in vitro localization in living or in paraformaldehyde fixed cells using fluorescence microscopy. The cell nucleus and mitochondria were stained using the vital-dye Hoechst33342 (blue for the nucleus) and the transfected Matrix-roGFP (green for mitochondria), respectively. This multiple staining allowed the intracellular localization of the TRITC-TiO2 NPs (by its red emitting fluorescence) 20 h after exposure. NPs were only found in the cytoplasm of exposed cells with no detection in the nucleus. NPs were randomly localized in the perinuclear region of the cytoplasm and totally excluded from the mitochondria (no overlapping between TRITC and GFP signals).
Although fluorescence microscopy is very useful to localize NPs inside exposed cells, it is not able to assess the exact number of NPs per cell. The main difficulty of fluorescence microscopy concerning the quantification of NPs is linked to the uncertainty about (i) the number of fluorophores attached to a given NP and the bleaching stability of the chosen fluorophore during the observation and (ii) the aggregation state of the NPs inside the cell.
Figure 1: in vitro and in situ fluorescence imaging of U20S transgenic cells expressing Matrix-RoGFP and exposed to TRITC-TiO2 NPs. U2OS cells (top) marked with Hoechst33342 (blue), Matrix-roGFP (green) are exposed to 4 µg.cm-2 TRITC-labeled TiO2 nanoparticles (red) for 20 h. Observations indicate that TiO2 NPs aggregate in cells in a perinuclear region. Scale bar: 10 µm. Please click here to view a larger version of this figure.
To overcome these shortcomings, nuclear microprobe analysis techniquesprovide a complementary approach to the conventional optical microscopy due to their sensitivity to the NPs which prevents the use of any intermediate signal like fluorescence from a grafted dye. Furthermore, they are also fully quantitative, providing data about (i) the sub-cellular biochemical content that is otherwise unknown, and (ii) the intracellular quantity of NPs at the single cell level.
Cryofixation of cells after live imaging.
The highest constraint in performing nuclear microprobe analysis is to work under vacuum conditions. We have developed a cell fixation protocol enabling the preservation of the biological ultrastructure and the biochemical integrity of the biological specimen. Chemical fixation is known to modify the trace element composition of cells because it requires the replacement of their cellular medium by a polymer used to preserve the cellular ultrastructure. Moreover, the removal of water also releases free ions and other species, which modifies the overall sample composition. Hence, it becomes mandatory to give priority to a physical fixation method, notably cryogenic methods. These cryogenic procedures induce a swift cessation of the cellular activity and this, in the millisecond time scale.
Nuclear microprobe analysis microscopy and quantification of NPs at the cellular scale.
Scanning transmission ion microscopy (µ-STIM) and Particle-induced X-ray emission (µ-PIXE) analysis were performed on samples after cryofixation and dehydration to obtain precise quantitative data on their elemental chemical composition.
µ-STIM images revealed the local differences in density and allows the detection of cell structures such as the nucleus and cytoplasm. Although the beam lateral resolution enables the observation of dense structures as narrow as 300 nm wide, like thin aggregates visible here in the cytoplasm, the STIM methods cannot discriminate between NP aggregates and other dense cellular structures. This is because, like for transmission electron microscopy (TEM), the physical process leading to variation in transmitted energy is the interaction of the incoming ion with the atomic electron cloud. Unlike TEM analysis however, because the entire cell volume is analyzed, local thickness variations prevent discrimination between high-Z structures and a local increase of cellular density.
Figure 2: Images of density and elemental distribution obtained by µ-STIM and µ-PIXE on cryo-fixed U2OS cells. U2OS control cells (up) are compared to exposed cryo-fixed U2OS cells (exposed to 4 µg.cm-2 TiO2 NPs, down) and observed using nuclear microprobe analysis/microscopy. STIM microscopy (left, grayscale maps) revealed dense intra- or extra-cellular structures (nucleus, salt aggregates, nanoparticles). The spatial resolution (300 nm) is comparable to fluorescence microscopy and shows structures such as NP aggregates in the perinuclear region. Identification of structures based only on their density may nevertheless be ambiguous. The µ-PIXE elemental maps of K, P and Ti (thermal color scale) are complementary to µ-STIM maps. They can be used to ensure the presence of NPs in cells. Each cell can be individually analyzed in terms of element concentration (see Figure 3). Scale bars: 10 µm. Color scales range from minimum (blue) to maximum intensity (gray). Please click here to view a larger version of this figure.
As illustrated in Figure 2, the µ-STIM rendering allows the recognition of individual cells within both a population and also intracellular sub-compartments such as the nucleolus and nucleus. Unfortunately, and as mentioned previously, NPs could not always be detected using µ-STIM reconstruction.
Particle-induced X-ray emission (µ-PIXE) analysis provides not only the chemical composition of the sample but also their elemental mapping (Figure 2). During the interaction with the exciting beam, the chemical elements undergo atomic excitation-de-excitation processes that eventually lead to the emission of a photon which exhibits the characteristic energy of the atomic number of the excited element. A characteristic peak spectrum is built from the sum of all the emitted photon events and is considered a chemical signature of the sample.
Standard experimental setups and detectors used for µ-PIXE experiments allow simultaneous quantification of all elements heavier than Na with a 1 to 10 µg.g−1 dry mass detection limit. Accuracy in measuring elemental concentrations is usually limited to around 20% due to charge collection and detector efficiencies.
In this study, the distribution of elements like potassium and phosphorus and to quantify the intracellular amount of TiO2 NPs with titanium mapping is observed by nuclear microprobe analysis. Chemical element maps are computed after the photons are sorted according to the beam position at the timing of recording and the selection of an energy window centered around a specific element. Maps are representative of the number of detected events at the beam position and are quantitative. Both noise and background are numerically simulated and filtered out. Furthermore, chemical mapping can be used to extract the local PIXE spectrum required for quantification.
As illustrated in Figure 2, phosphorus is homogenously distributed in the cell with, as expected, a much higher concentration in the nuclear area. Potassium is homogeneously distributed in the cell volume. Titanium is located in the cytoplasmic perinuclear region in the form of aggregates, as previously observed using fluorescence microscopy (Figure 1). NPs displayed the same perinuclear localization whatever their surface state: functionalized (Figure 1) or native (Figure 2). Meanwhile, no trace of titanium was detected in control cells confirming that the titanium distribution observed by µ-PIXE must be attributed to the TiO2 NPs, in agreement with our previous analyses by fluorescence microscopy.
In addition, as illustrated in Figure 2, it is possible to extract the intracellular distribution of NPs and quantitative NPs concentrations from specific regions of interest. Based on the STIM maps and in correlation with the phosphorus/potassium distributions, single cell analysis is possible.
Figure 3: Single cell quantitative analysis using µ-PIXE. Individual X-ray spectra calculated for cells shown in Figure 2 can be fitted in order to determine the element concentration at the cellular level. This feature is particularly interesting for NP analysis where cellular concentrations usually show strong variations inside the same population. For example, for the same mean exposure, the Ti concentrations range from 0.2 up to 1.8 µg.cm-2. Controls correspond to untreated cell populations. Exposure dose: 4 µg.cm-2. Boxplots represent the distribution of individual cellular concentrations with median value (horizontal line) and bars extending toward lowest and highest measured values. Control cells: N=14; Exposed cells: N=16.
Accordingly, we have not only quantified the average content of titanium in a cell population but also shown the titanium distribution per cell in one population in a specific experimental condition. The median content of titanium measured here is quite low (500 ng.cm-2) as compared to the 4 µg.cm-2 exposure dose of the cell population (Figure 3) and variation between cells is large (Ti concentrations range from 0.2 up to 1.8 µg.cm-2 according to the analyzed cells). We also noticed an increase of intracellular ions such as potassium and calcium in exposed samples suggesting a cellular alteration homeostasis induced by the presence of TiO2 NPs, as previously described by several authors.21,27
We describe a method providing useful information beyond what is possible with other imaging techniques, especially at the subcellular level. In addition to its imaging ability, nuclear microprobe analysis also offers possibilities of quantification of chemical elements entering in the composition of a biological sample. In the present work, we studied human cell populations and focused down to the analysis of a chosen region of interest based on a single cell exposed to TiO2 NPs. Its combination with other techniques provides both morphological cellular imaging and precise quantitative data on the elemental chemical composition.
To successfully apply nuclear microprobe analysis, it is mandatory to respect the following points to avoid potential pitfalls. First, it is imperative to use a cryogenic protocol for the cell fixation in order to retain its ultrastructure and its biochemical integrity. Second, it is also mandatory to perform analysis of thin samples with thickness below 20 µm. If needed, sectioning of cryofixed samples could be performed. Samples should absolutely be kept frozen. Third, it is also important to keep in mind that nuclear microprobe analysis reveals a two-dimensional representation of biological samples. Thus, the chemical element distribution obtained is a two-dimensional projection that could possibly introduce misinterpretations. This limitation will be bypassed in the future by the use of tomographic acquisition.
Nuclear microprobe analysis also has limitations. It has to be stressed that its main constraint is the need to perform analysis under vacuum. Therefore, it is imperative to use cell fixation protocols that preserves cells ultrastructure and biochemical integrity. It is therefore necessary to test the resistance of the biological samples to the cryogenics procedure (without the addition of chemical resin). This could limit the use of nuclear microprobe analysis.
Another limitation is the accessibility to the facilities for carrying out nuclear microprobe analysis. The assigned beam times are therefore sometimes limited, and this is an additional constraint for this kind of time-consuming experiment. Several hours are often needed for one acquisition.
This technique is different from other analytical methods, including microscopy, mass spectrometry (MS), inductively coupled plasma MS (ICP-MS), liquid chromatography MS (LC- MS), and radioactive isotope. The latter are indeed used to estimate the cellular dose of chemical elements but they are only able to provide information at a macroscopic scale i.e. on a macroscopic amount of a sample. None of them can give access, as nuclear microprobe analysis does, to a precise detection and mapping of a subcellular dose of specific chemical elements (ions, metal or metal oxide NPs). These data help accessing to a further systematic study of dose-response evaluation.
The precise estimation of the dose when studying the internalization of NPs in cells is crucial from both quantitative NP toxicology and pharmacology points of view. As suggested by the large discrepancy in the observed NP contents, which shows a 10-fold difference between the minimum and maximum observed concentrations (Figure 3), the mean cellular concentration might not be a relevant parameter to describe the phenomenon of particle exposure. This is particularly true when a threshold effect is supposed to take place because inhomogeneous dose exposure could lead to contradictory observations. Since the fractionated nature of nanoparticles appears clearly at the cellular level, this study therefore poses again the question of the relevance of methods based on analyzing global variables in addressing questions around the behavior of cells exposed to inhomogeneous doses of contaminants.
As illustrated in the case studied here, observation and quantification of NPs within individual cells allow us to better understand the bioaccumulation of endogenous/exogenous elements such as metal oxide NPs. This is a critical task for further applications of NPs in biomedicine, where a poor understanding of the underlying NP distribution in cells could lead to misinterpreted results.
This protocol highlights the suitability of using nuclear microprobe analysis with other techniques for future assessments of NP interactions with biological specimens. The quantitative approach provides information about the impact of such NPs in terms of detection, identification, localization, and quantification at the level of one single cell.
The authors have nothing to disclose.
We thank Serge Borderes for directing and editing of the video. The French National Research Agency supports the research program TITANIUMS (ANR CES 2010, n° CESA 009 01). The CNRS and the European Community as an Integrating activity provided the “Support of Public and Industrial Research Using Ion Beam Technology (SPIRIT)” under the EC contract n° 227012. This work has been supported by Marie Curie Actions – Initial Training Networks (ITN) as an “Integrating Activity Supporting Postgraduate Research with Internships in Industry and Training Excellence” (SPRITE, D1.3) under EC contract no. 317169. The C’NANO Grand Sud Ouest and the Region Aquitaine support the research program TOX-NANO (n°20111201003) and the research program POPRA (n° 14006636-034).
Cell culture | |||
U2OS | ATCC, LGC STANDARDS | ATCC HTB-96 | |
Medium MCCOY 5A w/o L-Glutamine | Dominique DUTSCHER | L0211-500 | |
FBS 500 mL | Dominique DUTSCHER | 500105U | |
Penicillin/Streptomycin | ThermoFisher Scientific | 11548876 | |
L-Glutamine 200 mM, 100 mL | Invitrogen | 25030024 | |
Geneticin, 20 mL | ThermoFisher Scientific | 10092772 | |
Trypsin-EDTA 0.25% (v/v) 500 mL | ThermoFisher Scientific | 11570626 | |
Viromer Red | Lipocalyx | VR-01LB-01 | |
Matrix-roGFP Plasmid | AddGene | #49437 | |
Hoechst 33342 | ThermoFisher Scientific | H3570 | Handle with care |
NPs preparation | |||
TiO2 P25 AEROXIDE | Degussa/Evonik | ||
Tetramethylrhodamine isothiocyanate (TRITC) | SIGMA-ALDRICH | T3163 | Surface modification of NPs |
Sample preparation | |||
Polycarbonate foil | Goodfellow | CT301020 | |
Polyether Ether Ketone support (PEEK) | Matechplast | A-239-4047 | |
Ethanol, ACS absolute | SIGMA-ALDRICH | 02860-6x1L | |
Chlorform, Anhydrous, 99% | SIGMA-ALDRICH | 372978-1L | Caution toxic |
Formvar 100 g | Agar Scientific | AGR1201 | Harmful. Use in a concentration of 10 µg per mL of chloroform |
NaOH | SIGMA-ALDRICH | S5881-500G | |
Sample fixation | |||
Powder, 95% Paraformaldehyde | SIGMA-ALDRICH | 158127-500G | Caution toxic. Use as a 4% solution in PBS |
PBS (pH 7.4, without Ca2+ and Mg2+) | ThermoFisher Scientific | 11503387 | |
Prolong Gold Antifade Reagent | ThermoFisher Scientific | P36934 | |
Triton X-100 | SIGMA-ALDRICH | 93443 | Harmful |
Sample cryofixation | |||
Liquid nitrogen | air liquids sante | Harmful | |
Methylbutane >=99% | SIGMA-ALDRICH | M32631-1L | Caution toxic |
Aluminium transfer plate | Home-made | ||
Distilled and deionized water | Home-made | Produced in the laboratory using the Barnstead Smart2Pure system | |
Parafilm | VWR | 52858-000 | |
Equipment | |||
Barnstead Smart2Pure | ThermoFisher Scientific | 50129870 | |
Biosafety bench, class II | ThermoFisher Scientific | MSC-Advantage | |
TC20 automated cell counter | Biorad | 145-0102SP | |
Counting slides 2 wells | Biorad | 1450016 | |
PIPS detector, 25 mm2, 12 keV energy resolution @5.5 MeV | Canberra | PD25-12-100AM | |
High-resolution Si (Li) solid-state detector,145-eVenergy resolution, @Mn-Kα | Oxford Instruments | ||
Everhart-Thornley type secondary electron detector (SED) | Orsay Physics | 1-SED | |
XRF Calibration Standard sodium or Chlorine as NaCl | Micromatter | 34381 | |
XRF Calibration Standard Magnesium as MgF2 | Micromatter | 34382 | |
XRF Calibration Standard Aluminium as Al metal | Micromatter | 34383 | |
XRF Calibration Standard Silicon as SiO | Micromatter | 34384 | |
XRF Calibration Standard Sulfur as CuSx | Micromatter | 34385 | |
XRF Calibration Standard Calcium as CaF2 | Micromatter | 34387 | |
XRF Calibration Standard Titanium as Ti metal | Micromatter | 34388 | |
XRF Calibration Standard Iron as Fe metal | Micromatter | 34389 | |
Sonicator 750W | Sonics Materials | 11743619 | |
3MM microprobe | Bioblock scientific | 220-05 | |
Lyophilizer in vacuum | Elexience | EK3147 | |
Optical microscope Zeiss AxioObserver Z1 | Carl Zeiss MicroImaging, GmbH | 431006-9901 | |
Motorized stage xy | Carl Zeiss MicroImaging, GmbH | 432031-9902 | |
EC Plan-Neofluar 20X, NA 0.50 Ph2 M27 objective | Carl Zeiss MicroImaging, GmbH | 420351-9910 | |
Plan-Apochromat 63X, NA 1,40 Ph3M27 objective | Carl Zeiss MicroImaging, GmbH | 420781-9910 | |
Zeiss filterset 02 | Carl Zeiss MicroImaging, GmbH | 488002-9901 | |
Zeiss filterset 38HE | Carl Zeiss MicroImaging, GmbH | 489038-9901 | |
Zeiss filterset 31 | Carl Zeiss MicroImaging, GmbH | 000000-1031-350 | |
Chemical fume hood | Erlab | Captair SD321 | |
Particle accelerator | HVEE | singletron | |
Software | |||
ImageJ software | National Institutes of health, USA | ImageJ 1.51 | |
SimNRA software | Max-Planck-Institut für Plasmaphysik, Germany | SIMNRA 6.06 | |
Gupix software | Guelph university, Canada | GUPIXWIN 2.2.4 |