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Millex gs filter

Manufactured by Merck Group
Sourced in United States

The Millex-GS filter is a sterile, single-use syringe filter designed for the filtration of aqueous solutions. It is constructed with a high-quality polyvinylidene fluoride (PVDF) membrane that provides effective filtration of particulates and microorganisms. The filter has a pore size of 0.22 µm, making it suitable for a wide range of laboratory applications requiring sterile filtration.

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8 protocols using millex gs filter

1

Radiotracer Dosimetry for AMS Studies

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Ciprofloxacin was obtained via the hospital pharmacy from Bayer Austria (400 mg/200 mL infusion solution). [14C]Ciprofloxacin (labeled in the 2-position of the quinoline ring, molar activity: 2.2 GBq/mmol, radiochemical purity: 98.2%) was obtained from Hartmann Analytic GmbH (Braunschweig, Germany). For the i.v. injection, [14C]ciprofloxacin (7 kBq, 1.1 µg) was dissolved in 10 mL of physiological saline solution and filtered through a sterile Millex-GS filter (0.22 µm; Millipore Corporation, Bedford, MA, USA).
No formal dosimetry calculation was performed for [14C]ciprofloxacin. Because of the very high sensitivity of AMS, the administration of only very low 14C amounts is required (7 kBq in the current study). In addition, as the energy of the β particles emitted in the decay of 14C is relatively low (0.156476 MeV), AMS microdosing studies usually fall within risk category I (trivial risk, total effective dose < 0.1 mSv) according to the International Commission on Radiological Protection Publication 62 “Radiological Protection in Biomedical Research” [30 ]. However, an intravenously injected 18F-labeled radiotracer for PET (400 MBq) typically gives a total effective dose in the range of 5–10 mSv, corresponding to risk category IIb (minor to intermediate risk) in the International Commission on Radiological Protection publication 62 [30 ].
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2

Pharmacokinetics of CPZEN-45 by Different Routes

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Animals were randomly divided into three groups; each group received CPZEN-45 at a dose of 1 mg/kg in solution by the IV (n = 7) or SC (n = 6) routes or CPZEN-45 powders (1 mg/kg) by the pulmonary route (INS; n = 6) (Table 1). CPZEN-45 solutions were prepared by dissolving a weighed amount of CPZEN-45 hydrochloride salt in water for injection and filtering the solution through a 0.22-μm Millex GS filter (Millipore, Cork, Ireland). To administer the CPZEN-45 powders by INS, each animal was first anesthetized, and the trachea was visualized with the help of a laryngoscope. The tube of a small-animal insufflator (Penn Century Inc., Wyndmoor, PA, USA) was inserted into the trachea, and the CPZEN-45 powder was aerosolized into the airways of the animal with the help of air from an empty 10 mL syringe [19 (link)]. Blood samples (0.3 mL) were collected from each animal into heparinized micro-centrifuge tubes at 0 (prior to dosing), 0.08, 0.25, 0.50, 1, 1.5, 2, 3, 4, and 5 h after administration of the single dose CPZEN-45 by the different routes. Warm sterile saline solution was used to replace the volume of blood drawn after each sample collection to maintain the volume of distribution constant in each animal.
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3

Elemental Analysis of Fish Powder

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Fish powder samples were incubated with 6 mL of aqueous nitric acid (6.9% v/v) in a Thermomixer comfort (Eppendorf Japan, Tokyo, Japan). Collected supernatants were filtered through a Millex GS filter (0.22 mm, EMD Millipore, Billerica, MA) using SPS5510 (Hitachi High-Tech Science Corporation, Tokyo, Japan). The sediment samples were freeze-dried, and 10 mg of the powder was incubated with 1 mL of methanol at 50 °C for 15 min. After centrifugation (14000 rpm, 5 min), the supernatants were removed and 2 mL of aqueous nitric acid (6.9% v/v) was added, and the sample incubated at 50 °C for 15 min. The supernatants were collected after centrifugation (14000 rpm, 5 min), and the extraction using 2 mL of aqueous nitric acid (6.9% v/v) was repeated three times. The water samples were diluted to ten times using milli-Q water, and then used for ICP-OES analyzes. The ICP-OES analysis was conducted using an SPS5510 instrument, with a range of wavelengths from 167 to 785 nm and 74 applicable elements. The ICP-OES data is available in Table S5.
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4

Groundwater Geochemical Tracers: V and Sr

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Owing to their low abundance and very diverse concentrations and isotopic ratios in different rocks and minerals, V concentrations and Sr isotopes are powerful geochemical tracers of groundwater flow and proxies of groundwater residence times118 ,119 . Vanadium in groundwater originates from alkaline rocks in contact with oxidized water, and is found to increase with groundwater residence times16 ,70 (link),71 (link),120 . Vanadium dissolution is geochemically similar to Sr enrichment in groundwater. In groundwater hydrology, the 87Sr/86Sr isotopic ratio is widely employed as a tracer to track exchanges with different rocks and minerals119 ,121 –124 . As water–rock exchange processes depend on time, V concentrations and 87Sr/86Sr ratios tend to correlate with, and (under certain constraints) might be indicative of, groundwater residence times46 (link),51 ,125 .
Vanadium water samples were filtered using a 0.22 μm Millex-GS filter (Merck Millipore) and acidified to a pH below 2 using nitric acid. The filters were washed with 10% hydrochloric acid and 0.1 M nitric acid before use. Vanadium concentrations were analysed using a polarized Zeeman Z-3700 atomic absorption spectrophotometer (Hitachi High-Tech) at Shizuoka University after dilution with 0.1 M nitric acid by 10% (typical analytical error ±4%). Strontium isotopic ratios were taken exclusively from the literature.
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5

Water Isotope and Ion Analysis

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For the analysis of stable water isotopes and major ions, samples were filtered with a 0.22 μm Millex-GS filter (Merck Millipore) and stored at −20 °C and 4 °C, respectively, before analysis. Major ion compositions were analysed at Shizuoka University using a Dionex ICS-3000 ion chromatograph (Thermo Fisher). Stable water isotopes were analysed by Shoko Science Co Ltd (using a Picarro L2120-I cavity ring-down spectrometer, Picarro, Inc.), normalized to the VSMOW and reported in δ notation117 (typical analytical errors are ±0.2‰ for δ2H and ±0.05‰ for δ18O).
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6

Outer Membrane Vesicle Purification

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OMV purification was performed following the protocol used by Martora et al. with some slight modifications [13 (link)]. Briefly, three K. pneumoniae strains were grown in LB broth (600 mL, 37 °C, 180 rpm) to an OD600 nm value of 1. The bacterial cells were decanted through centrifugation and supernatants were filtered at 0.45 µm and 0.22 µm (Millex-GS filters, Millipore, Darmstadt, Germany). The cell-free supernatants were centrifuged at 100,000× g for 2 h at 4 °C (centrifuge Optima XPN-100 Beckman Coulter and rotor 70Ti, Palo Alto, CA, USA). The pellets were washed in sterile PBS1X by ultracentrifugation and re-suspended in 200 µL of PBS1X. The sterility of the OMVs was checked on LB agar plates. The purified OMVs were stored at −20°C after dynamic light scattering (DLS) analysis.
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7

Virus Isolation from Mosquito Pools

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A. albopictus C6/36 cells and BHK-21 cells were used to isolate viruses from 220 pools of 18,560 mosquitoes. Specifically, suspensions of mosquito homogenates were filtered through 0.22-µm Millipore Millex-GS filters (Millipore Corp, Billerica, MA, USA) and used to infect C6/36 and BHK-21 cells at 28 °C and 37 °C, respectively, under 5% CO2. CPEs were evaluated every 8 h in three blind passages after incubation for 24 h and observation over the next 7 days. A positive virus isolation from a specimen was defined as one in which 70% CPE was observed at 2 days post-infection.
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8

Bacillus subtilis Zn(II) Adsorption

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Zn(II) adsorption
by Bacillus subtilis suspensions
was studied in batch experiments performed at 25 °C ± 1
and in 0.1 M Na(Cl) ionic medium. Samples from the bacterial parent
suspensions were transferred into 10 mL tubes, and the pH was varied
by adding aliquots of HCl and NaOH solutions prepared in the same
ionic medium from automatic burets. Aliquots of the ZnCl2 solution in 0.1 M Na(Cl) were added at the end in order to have
a total Zn(II) concentration in the samples corresponding to a ratio
[Zn2+]/bacterial biomass of 0.12–0.14 mmol/g (dry
weight) (corresponding to a total concentration Zn(II) in solution
approximately 1 mM). The samples were placed on an end-over-end rotator
and centrifuged for 20 min at 2880g after 24 h equilibration
time at 25 °C ± 1 and remeasuring of pH. Following centrifugation,
the supernatants used for AAS analysis were separated from the paste,
filtered through 0.22 μm membranes (MILLEX GS filters, MILLIPORE),
acidified, and stored in the refrigerator (4 °C) until analysis.
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