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0.45 μm filter

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The 0.45 μm filter is a laboratory filtration device designed to remove particulates and microorganisms from liquid samples. It has a pore size of 0.45 micrometers, which allows the passage of dissolved molecules while retaining larger particles and microbes.

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16 protocols using 0.45 μm filter

1

IPNV Detection in Challenged Fish Fry

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Fry mortalities and survivors from the challenged tanks and control tanks were tested for the presence of IPNV using different methods. Fry were weighed, homogenised using sterile pestle, mortar and sand then diluted 1:10 in cellculture medium. The homogenate was centrifuged at 2500 × g for 15 min. at 4 °C then the supernatant removed and filtered through 0.45 μm filter (Whatman) before inoculation onto 24 h old confluent monolayers of CHSE-214 cells in 96-well cell culture trays for titration according to [73 (link)]. Culture trays were incubated at 15 °C and titres read after 7 days. Wells showing positive cytopathic effect (CPE) for each sample were further tested by ELISA (Test-Line) to confirm the presence of IPNV. Subsequently, for the determination of viral load in the samples used for the microarray experiment, an RT-QPCR assay applied in an accredited commercial laboratory (Integrin Advanced Biosystems, UK) was used.
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2

Water Sample Collection and Preparation

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The method was tested on seven different natural water samples. The origin of the samples was divided into three distinct categories: river samples, bottled samples, and tap water samples. Four bottled water samples were purchased from local stores in the Thessaloniki city center. Two river water samples were collected in the Epirus region (NW Greece), from the Louros and Acheron rivers, stored in glass containers of 500 mL each, and filtered through a Whatman 0.45 μm filter to remove any suspended solids. Finally, the tap water sample was collected from the water supply system of the Aristotle University of Thessaloniki campus. All samples were stored at 4 °C in the refrigerator.
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3

Preparation of Aqueous OS-EL Solution

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OS-EL (100 mg) was dissolved in 50 mL of deionized water and sonicated for 15 min. Working sample solution of concentration of 2 mg/mL was prepared by diluting the stock solution with deionized water. The sample was filtered through a 0.45 μm filter (Whatman).
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4

Molecular Weight Characterization of Polymer Samples

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Specimens were dissolved in chloroform (Sigma-Aldrich, St. Louis, MO) at a concentration of 20 mg/mL under mild agitation at room temperature and filtered by injection through a 0.45 μm filter (Whatman, Kent, UK). The resulting solution was assayed for molecular weight by gel permeation chromatography (GPC) based on previously reported methods [17 (link), 24 ]. The GPC system (Waters, Milford, MA) consisted of a pump (Waters Model # 155), injection module (Waters # 717), and refractive index detector (Waters Model # 410). GPC was performed (n = 3) at a flow rate of 1 mL/min and temperature of 30 °C using a Phenogel column (300 × 7.80 mm, 5 μm particle size, Waters) and calibrated using linear PMMA standards with molecular weights ranging from 2.58 to 981 kDA (Waters, Milford, MA). Number average molecular weight (Mn), weight average molecular weight (Mw), and polydispersity index (PI) were measured and reported.
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5

Carbapenem-resistant Pseudomonas aeruginosa Isolation

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Effluents from both WWTPs were sampled monthly for one-year period. Effluent water was refrigerated until further processed in the laboratory, usually within 6 hours of collection.
For selective isolation of carbapenem-resistant P. aeruginosa 100 ml of effluent water was filtered through 0.45 μm filter (Whatman). Filters were plated onto in-house selective medium (cetrimide agar (Merck)) supplemented with imipenem with a final concentration of 4 μg/mL) and incubated at 42°C for 48-hours.
After incubation up to ten suspected P. aeruginosa colonies were subcultured and identified by MALDI-TOF. All isolates confirmed as P. aeruginosa were submitted for identical antibiotic susceptibility testing as described above for clinical strains.
Isolates of P. aeruginosa resistant to either imipenem or meropenem or both were stored at -70°C for further processing.
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6

Comprehensive Soil Analysis Protocol

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Prior to analysis, soil subsamples were air-dried and later passed through a 2 mm mesh screen. The following parameters were measured for the soil subsamples (five subsamples from each plot): pH in H2O and KCl deionised water suspension (PN-ISO 10390:1997), humid acids (Stevenson 1994 ), total Kjeldahl nitrogen (PN-ISO 11261:2002), total organic carbon using a Multi N/C H1300 Analitykjena (PN-ISO 10694:2002), available phosphorus using the Enger-Riehm method (Karczewska and Kabała 2008 ), CEC (Cation Exchange Capacity) according to Kappen's method (Karczewska and Kabała 2008 ). Soil solution samples were filtered with a Whatman 0.45 μm filter prior to analysis. Soil material and plant material (five repetitions) were digested using hot aqua regia (PN-ISO 11047:2001). Then the digested experimental material and pore soil solution were analyzed for the presence of Cd, Pb, and Zn using inductively coupled plasma optical emission spectrometry (ICP-OES; Thermo apparatus). On the basis of the content of heavy metals in shoots and roots of trees and the concentration of trace elements in the soil were calculated following indicators:
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7

Dissolution Profiling of LCM and LCM-E100 MPs

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The dissolution profile of LCM and prepared LCM-E100 MPs was evaluated using a USP dissolution test apparatus II (Hanson elite 8, Chatsworth, CA, USA). The number of prepared MPs corresponded to 50 mg of LCM. The formulations were suspended in 900 mL of distilled water and in a buffer solution of pH 1.2, separately [16 (link),17 ]. A paddle speed of 50 rpm and temperature of 37 ± 0.5 °C were maintained during the experiment. At predetermined time intervals (0, 5, 10, 15, 30, 45, 60, and 120 min), 3 mL of sample was collected and passed through a 0.45-μm filter (Whatman, Maidstone, UK). The aliquots were replaced with fresh dissolution medium. The concentration of LCM was analyzed by HPLC. All experiments were performed in triplicate.
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8

Formulation and Evaluation of FLBZ Delivery

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The FLBZ HPBCD-based solution was prepared by dissolving FLBZ (0.1%) and HPBCD (10%) in deionized water. The pH of the formulation was adjusted to 1.2 using HCl (25 mM). The formulation was shaken until total dissolution of the drug and then was filtrated through a 0.45 μm filter (Whatman, NJ, USA). The final FLBZ concentration was confirmed by HPLC. The Tween 80-based formulation was prepared by dissolving FLBZ (0.25%) in Tween 80. The FLBZ-suspension was prepared by addition of FLBZ (0.1%) and CMC (0.1%) in deionized water (pH = 6.0) with shaking for 6 h. The FLBZ-CMC suspension was vigorously shaken immediately before administration to pigs. FLBZ formulations were freshly prepared and maintained under refrigeration (3–5 °C).
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9

HPLC Analysis of Promising B. hispida Extract

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Qualitative and quantitative analyses of the most promising B. hispida extract were performed using an HPLC system (Prominence LC2030C, Shimazu, Japan). A Knauer® vertex III reversed-phase HPLC column C18 (250 mm × 20 mm) (KNAUER Wissenschaftliche Geräte GmbH, Berlin, Germany) was used as the stationary phase. A gradient system was used as an analytical method with a detector at a wavelength of 360 nm. The mobile phase consisted of A (0.1% acetic acid in water) and B (acetonitrile) with a flow rate of 1.0 mL/min for 33 min. Gradient elution of the mobile phase was carried out as follows: 0.01 min, 95% A; 2 min, 95% A; 7 min, 80% A; 22 min, 70% A; 23 min, 95% A; and 33 min, 95% A. The analytical samples were dissolved in absolute ethanol and filtered through a 0.45 μm filter (Whatman, Marlborough, MA, USA) before analysis with an injection volume of 10 μL. B. hispida extract at 1.0 mg/mL was prepared for analysis. Rutin was used as a reference compound to analyze the active compounds in B. hispida extract. The retention time of rutin was approximately 17 min. The concentration of rutin in B. hispida extract was calculated from the peak area using a linear equation constructed from a standard curve of rutin (0.0 to 50 µg/mL).
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10

IPNV Detection in Fish Fry

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Fry mortalities and survivors from the challenged tanks and control tanks were tested for the presence of IPNV. Fry were weighed, homogenised using sterile pestle, mortar and sand then diluted 1:10 in cell culture medium. The homogenate was centrifuged at 2500 ×g for 15 min. at 4 °C then the supernatant removed and filtered through 0.45 μm filter (Whatman) before inoculation onto 24 h old confluent monolayers of CHSE-214 cells in 96-well cell culture trays for titration. Culture trays were incubated at 15 °C and titres read after 7 days. Wells showing positive cytopathic effect (CPE) for each sample were further tested by ELISA (Test-Line) to confirm the presence of IPNV. Subsequently, for the determination of viral load in the samples used for the microarray experiment, an RT-QPCR assay applied in an accredited commercial laboratory (Integrin Advanced Biosystems, UK) was used.
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