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Multisizer 3 particle counter

Manufactured by Beckman Coulter
Sourced in United States

The Multisizer 3 particle counter is a versatile instrument used for the accurate measurement and analysis of particle size and concentration. It employs the Coulter principle to provide precise data on the size distribution and number of particles within a sample, making it a valuable tool for various applications that require detailed particle characterization.

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8 protocols using multisizer 3 particle counter

1

Lipid-Coated Microbubble Synthesis and Characterization

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All the lipids were purchased from Avanti Polar Lipids, Inc. (Alabaster, AL, USA), including 1,2-dipalmitoyl-sn-glycero-3-phosphocholine (DPPC or C16), 1,2-distearoyl-sn-glycero-3-phosphocholine (DSPC or C18), 1,2-dilignoceroyl-sn-glycero-3-phosphocholine (DLiPC or C24) and 1,2-distearoyl-sn-glycero-3phosphoethanolamine-N-[methoxy(polyethylene glycol)2000] (DSPE-PEG2000). The perfluorobutane gas (PFB, 99 wt% purity) used for microbubble generation was obtained from FluoroMed (Round Rock, TX, USA).
The lipid-coated microbubbles as shown in Fig. 1A were prepared at a 9:1 molar ratio of lipids and lipopolymers (DSPE-PEG2000). They were generated using the probe sonication method and size selected to 4–5 μm in diameter using differential centrifugation, as described elsewhere [21 (link)]. A Multisizer III particle counter (Beckman Coulter Inc., Opa Locka, FL, USA) with a 30-μm aperture was used to measure the microbubble size distribution (Fig. 1B–C) and concentration. The final size-isolated (4–5 μm) microbubble suspension was stored at 4 ºC till the time of injection. All the microbubble samples used for this study were freshly prepared within 24 h to ensure experimental consistency.
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2

Lipid-Shelled Microbubble Size Isolation

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Lipid-shelled monodisperse microbubbles with three different diameter ranges (1-2, 4-5, and 6-8 μm) were prepared in-house and size-isolated using the differential centrifugation method according to a previously published protocol (Feshitan et al 2009 (link)). A Multisizer III particle counter (Beckman Coulter, Opa Locka, FL) with a 30-μm aperture was used to measure the size distribution and concentration. The concentration of microbubble solution was diluted using phosphate-buffered saline (PBS) to 8×108 numbers/ml prior to intravenous administration through the tail vein.
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3

Algae Exposure to Platinum Nanoparticles

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Algae were exposed to PtNPs (2 and 80 mg Pt/L) in triplicate 250 mL flasks with 75 mL suspension inoculated to10 5 cells/mL. A sample of 20 mL suspension from each replicate was taken after 2, 24 and 48 h incubation and filtered through a 3.0 µm nitrocellulose filter (Merck Millipore). The algal cells retained by the filter were gently washed with 20 mL medium before filters were digested in Teflon tubes (1 mL aqua regia at 90°C for 2 h). The Pt content was determined by ICP-MS analysis (Agilent 7700, Morges, Switzerland) after dilution with 5% (v/v) HCl (Baker, instar grade). The cell number for each replicate suspension was determined after 0, 2, 24 and 48 h incubation on a Coulter Multisizer III particle counter (Beckman-Coulter, Switzerland). Suspensions of PtNPs in media (80 mg Pt/L) without algae were applied as background controls, and treated as described above. The particle counts and Pt content of digested filters were all background corrected using data from these controls.
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4

Ploidy Assessment by Flow Cytometry

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Strain ploidy level was assessed using SYTOX® Green (Invitrogen) fluorescence and flow cytometry according to Delobel and Tesnière65 , using an Accuri C6TM flow cytometer. A single colony was selected and grown overnight in liquid YEPD with shaking at 150 rpm. Cells in exponential phase were collected by centrifugation and then re-suspended in 1 mL water. Eight ml of 75% ethanol were added and fixation was performed overnight at 4 °C. Fixed cells were harvested by centrifugation and washed with 1 mL PBS 1X. Cells were re-suspended in 500 μL RNAse A (Qiagen, Paris, France) solution (2 mg/mL RNAse A in 10 mM Tris-HCl, 15 mM NaCl) and incubated at 37 °C for 1 h and finally re-suspended in 200 μL of proteinase K (Roche, Paris, France) solution (1 mg/Ml in PBS 1X). After a 1 h- incubation at 50 °C, cells were collected by centrifugation, re-suspended in 500 μL PBS 1X, sonicated for 15 s, and stored on ice until analysis. Fifty µL of cell suspension were added to 200 μl of SYTOX® Green solution (1.25 µM SYTOX® Green in PBS 1X). Analysis was performed with a Multisizer 3 Particle Counter (Beckman Coulter, Paris, France). The FL1 detector (530/30 nm) was used for the acquisition of SYTOX® Green fluorescence, as this dye is taken up by cells in a manner stoichiometric to the amount of nuclear DNA.
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5

Preparation of Particulate Matter Test Samples

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Arizona test dust (ISO 12103-1) is used to make the PM test samples. The average diameters of PMf and PMc are 1.256 ± 1.309 µm and 7.657 ± 1.286 µm, respectively. The size distributions of PMs are measured by using the Multisizer 3 particle counter (Beckman Coulter, USA). The polydispersity index (PDI) is defined as the square of mean diameter of PMs divided by their standard deviation. The PDI values of PMf and PMc are 1.086 and 0.0282, respectively. Two reference samples of PMf and PMc with mass concentration values of 20 µg/ml are prepared by mixing PMs and distilled water. 20 mg of PM is measured by using an electronic balance (CAS, Korea) and then mixed with 1L of distilled water in a 1L wide neck bottle (Azlon, UK) to make two reference samples of PMf and PMc. The two reference samples and distilled water are then mixed in 30 ml square-shaped transparent bottles (Triforest, USA) at different volume ratios using 10 ml sterile syringes (Shinchang Medical, Korea) to prepare PM test samples with various concentration ratios of PMf and PMc.
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6

Culturing C. reinhardtii for Trace Metal Studies

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C. reinhardtii is a green microalga that is ubiquitous to fresh waters and is often used for water quality monitoring and studies examining the toxicology of pollutants in natural waters. Details on its specific culture and preparation for experiments involving trace metals can be found in Zhao and Wilkinson (2015). 22 In brief, wild type CC-125 (aka 137c) from the Chlamydomonas resource center was grown at 20°C under conditions of 12 h light/12 h dark (60 mmol s -1 m -2 ) using orbital shaking (100 rpm), until algae reached their mid-exponential growth phase in 4×diluted TAP. The cells were then washed 3x with a simplified exposure medium (see below) that contained no Ce. Cell concentrate was added to the exposure solutions in order to obtain 6.5-10 x 10 4 cells mL -1 (i.e. 0.15 cm 2 .mL -1 ). Cell concentrations and cell surface areas were measured using a Multisizer 3 particle counter (50 mm aperture; Beckman Coulter).
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7

Blocking FcγRIIIA to Mitigate ITP

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ITP was passively induced with a rabbit antiplatelet serum (Cedarlane, CLA31440) in FcγR-humanized mice using a method previously described in detail.12 Briefly, all treatments were administered IV through the lateral tail vein. To examine the in vivo effect of 17C02-albumin and 17C02-IgG2a, mice were treated with an equimolar amount (540 μM/mouse) of these molecules as well as human albumin as a negative control. For clarity, 2 different concentrations of these FcγRIIIA blockers as well as the albumin control were used in the blocking studies. The same equimolar amount of 3G8 (mouse IgG1) was also evaluated as a reference reagent. Body (rectal) temperature was then monitored using a rectal temperature probe (Kent Scientific) to assess adverse events. After 2 hours, the animals were bled via the saphenous vein to count platelets (as described in detail13 ), and ITP was induced with 15 μL of the rabbit antiplatelet serum. Animals were bled again 2 hours later via the saphenous vein, and the platelet number was enumerated by a Multisizer 3 particle counter (Beckman Coulter, Canada) as described in detail.12
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8

Quantifying Microbial Cell Abundances and Aggregates

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Cell abundances in the cultures were determined with the use of epifluorescence microscopy (Carl Zeiss AxioScope.A1). Glutaraldehyde-fixed samples were stained with the nucleic acid dye DAPI (4′,6-diamidino-2-phenylindole, 0.03 M, Sigma-Aldrich), and filtered onto gray 0.2 µm pore-size polycarbonate membranes (GVS Life Technologies, ME). Chlorophyll-a emission by M. polymorphus cells and DAPI-stained bacteria were visualized under 450–490 nm excitation and 380–400 nm, respectively.
Volume concentrations of micro-aggregates “suspended” in cultures (i.e., non-sinking particles with an equivalent spherical diameter [ESD] of 5–60 µm) were determined at every sampling period using a Multisizer 3 Particle Counter (Beckman Coulter, CA). Prior to fixation with glutaraldehyde, duplicate samples were diluted to a 1–10% final particle concentration with Isoton II diluent (Beckman Coulter, CA) and aggregates were measured and quantified with a 100 µm aperture tube. The volume concentration of aggregates was calculated in µm3 per mL.
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