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Cellulose ester membrane

Cellulose estr membranes are a class of semipermeable barriers composed of derivatized cellulose polymers.
These membranes are widely used in a variety of applications, including filtration, dialysis, and drug delivery.
They offer high permeability, good mechanical strength, and the ability to selectively transport molecules based on size and charge.
Researchers studying cellulose ester membranes often face challenges in identifying the optimal protocols and products from the scientific literature.
PubCompare.ai can help by leveraging AI-driven comparisons to streamline this process, enabling more reproducible and accurate results in cellulose ester membrane research.

Most cited protocols related to «Cellulose ester membrane»

Study sites. Four WWTPs were included in this study: two in the Mid-Atlantic region and two in the Midwest. The treatment steps and sampling locations at each of the treatment plants are illustrated in Figure 1.
Mid-Atlantic WWTP1 (Figure 1A) is a tertiary WWTP in an urban area that processes 681,390 m3/day of wastewater, with a peak capacity of 1.51 million m3/day. Mid-Atlantic WWTP2 (Figure 1B), a tertiary WWTP in a suburban area, processes 7,570 m3/day of wastewater and has a peak capacity of 45,425 m3/day. Tertiary wastewater treatment includes primary treatment (physical removal of solids), secondary treatment (biological treatment), and additional treatment that can include, but is not limited to, chlorination, ultraviolet radiation, or filtration. The incoming wastewater (influent) at both Mid-Atlantic plants includes domestic and hospital wastewater, and effluent (discharge) from both Mid-Atlantic plants is piped to landscaping sites for reuse in spray irrigation.
Midwest WWTP1 (Figure 1C) is a tertiary WWTP in a rural area that processes 1,363 m3/day of wastewater, with a peak capacity of 10,978 m3/day. The incoming water includes domestic wastewater and agriculturally influenced stormwater. Seasonal chlorination occurs in June, July, and August, and chlorinated effluent is piped to a landscaping site for reuse in spray irrigation. Midwest WWTP2 (Figure 1D), a secondary WWTP (with no on-site disinfection) in a rural area, processes 1,439 m3/day and has a peak capacity of 7,571 m3/day. Secondary wastewater treatment includes only primary treatment (physical removal of solids) and secondary treatment (biological treatment). The incoming water at this plant includes domestic wastewater, wastewater from a food production facility, and agriculturally influenced stormwater. Unchlorinated effluent is piped to an agricultural site for crop irrigation.
Sample collection. A total of 44 grab samples were collected between October 2009 and October 2010: 12 samples from Mid-Atlantic WWTP1; 8 from Mid-Atlantic WWTP2; 12 from Midwest WWTP1; and 12 from Midwest WWTP2. The timing of each sampling event was determined by the availability and schedule of the WWTP operators. The sampling time schedule and specific sampling locations for each plant are indicated in Tables 1 and 2 and Figure 1. Samples were collected in 1-L sterile polyethylene Nalgene® Wide Mouth Environmental Sample Bottles (Nalgene, Lima, OH), labeled, and transported to the laboratory at 4°C. All samples were processed within 24 hr.
Isolation. Membrane filtration was used to recover S. aureus and MRSA from wastewater samples. Briefly, 300 mL of each sample were vacuum filtered through a 0.45-µm, 47-mm mixed cellulose ester filter (Millipore, Billerica, MA). Filters were then enriched in 40 mL of m Staphylococcus broth (Becton, Dickinson and Company, Franklin Lakes, NJ), vortexed, and incubated at 37°C for 24 hr. A 10-µL loopful of each enrichment was then plated in duplicate on MRSASelect (Bio-Rad Laboratories, Hercules, CA) and Baird Parker agar (Becton, Dickinson and Company) for the isolation of MRSA and total S. aureus, respectively. Plates were incubated at 37°C for 24 hr. Resulting black colonies with halos on Baird Parker agar and hot pink colonies on MRSASelect were considered presumptive S. aureus and MRSA, respectively. These colonies were purified on Brain Heart Infusion (BHI) agar (Becton, Dickinson and Company) and archived in Brucella broth (Becton, Dickinson and Company) with 15% glycerol at –80°C. For quality control and quality assurance throughout the isolation process, S. aureus ATCC 43300 [American Type Culture Collection (ATCC), Manassas, VA] was used as a positive control and phosphate-buffered saline was used as a negative control.
Identification. S. aureus and MRSA were confirmed using Gram stain, the coagulase test (Becton, Dickinson and Company), the catalase test, and polymerase chain reaction (PCR). DNA extraction was carried out using the MoBio UltraClean® Microbial DNA Isolation Kit (Mo Bio Laboratories, Carlsbad, CA) following the manufacturer’s recommendations. For confirmation of S. aureus, we carried out PCR amplification of the S. aureus-specific nuc gene using NUC1 and NUC2 primers (Fang and Hedin 2003 (link)). For MRSA differentiation, we performed PCR amplification targeting the mecA gene, which encodes for methicillin resistance, using ECA1 and MECA2 primers, as previously described by Fang and Hedin (Brakstad et al. 1992 (link); Fang and Hedin 2003 (link); Smyth et al. 2001 (link)). The method was modified by including an internal control, using primers targeting the 16S rDNA genes, in a multiplex PCR assay (Edwards et al. 1989 (link)). PCR amplification consisted of an initial denaturing step of 95°C for 3 min, followed by 34 cycles of denaturing at 94°C for 30 sec, annealing at 55°C for 30 sec, and extension at 72°C for 30 sec, with a final extension at 72°C for 5 min.
Antimicrobial susceptibility testing. We performed antimicrobial susceptibility testing on all PCR-confirmed MRSA (n = 240) and MSSA (n = 119) isolates using the Sensititre® microbroth dilution system (Trek Diagnostic Systems Inc., Cleveland, OH) in accordance with the manufacturer’s instructions. Overnight cultures were transferred to sterile demineralized water (Trek Diagnostic Systems) to achieve a 0.5 McFarland standard. Then, 30 µL of each suspension was transferred to sterile cation-adjusted Mueller Hinton broth (Trek Diagnostic Systems) and 50 µL of the broth solution was then dispensed into GPN3F minimal inhibitory concentration (MIC) plates (Trek Diagnostic Systems Inc.) with the following antibiotics: erythromycin (ERY; 0.25–4 µg/mL), clindamycin (CLI; 0.12–2 µg/mL), quinupristin/dalfopristin (SYN; 0.12–4 µg/mL), daptomycin (DAP; 0.25–8 µg/mL), vancomycin (VAN; 1–128 µg/mL), tetracycline (TET; 2–16 µg/mL), ampicillin (AMP; 0.12–16 µg/mL), gentamicin (GEN; 2–16, 500 µg/mL), levofloxacin (LEVO; 0.25–8 µg/mL), linezolid (LZD; 0.5–8 µg/mL), ceftriaxone (AXO; 8–64 µg/mL), streptomycin (STR; 1,000 µg/mL), penicillin (PEN; 0.06–8 µg/mL), rifampin (RIF; 0.5–4 µg/mL), gatifloxacin (GAT; 1–8 µg/mL), ciprofloxacin (CIP; 0.5–2 µg/mL), trimethoprim/sulfamethoxazole (SXT; 1/19–4/76 µg/mL), and oxacillin+2%NaCl (OXA+; 0.25–8 µg/mL). Enterococcus faecalis ATCC 29212 and S. aureus ATCC 29213 strains were used for quality control. MICs were recorded as the lowest concentration of an antimicrobial that completely inhibited bacterial growth [Clinical and Laboratory Standards Institute (CLSI) 2010]. Resistance break points published by the CLSI were used (CLSI 2010). Multidrug resistance (MDR) was defined as resistance to two or more classes of antibiotics.
SCCmec typing. We used a multiplex PCR assay developed by Milheiriço et al. (2007) (link) to characterize the MRSA isolates (n = 240) by SCCmec type (Milheiriço et al. 2007 (link); Oliveira and de Lencastre 2002 (link)). SCCmec strains COL (type I), BK2464 (type II), ANS46 (type III), MW2 (type IVa), HAR22 (type IVh), and HDE288 (type VI) were used as positive controls for SCCmec typing.
PVL screening. All MRSA isolates, confirmed by possession of the nuc and mecA genes by PCR and an identifiable SCCmec type (n = 236), were screened for PVL by PCR of the pvl gene according to Strommenger et al. (2008) (link). S. aureus ATCC strain 25923 was used as a positive control.
PFGE. We performed PFGE on a subset of 22 MRSA isolates. To ensure a diverse, representative subset, isolates were selected using the following criteria: treatment plant, sampling date, SCCmec type, and each sampling location that had a positive sample. PFGE was based on the Centers for Disease Control and Prevention (CDC) Laboratory Protocol for Molecular Typing of S. aureus by PFGE (CDC 2011 ). We used SmaI (Promega, Madison, WI) to digest genomic DNA. Digested samples were run in 1% SeaKem® Gold agarose gels (Cambrex Bio Science Rockland Inc., Rockland, ME) in 0.5X TBE (tris-borate- EDTA) using a CHEF Mapper (Bio-Rad) for 18.5–19 hr at 200 V, 14°C, and initial and final switch of 5 and 40 sec. Cluster analysis was performed using BioNumerics software v5.10 (Applied Maths Scientific Software Development, Saint-Martens-Latem, Belgium) using Dice coefficient and the unweighted pair-group method. Optimization settings for dendrograms were 1.0% with a position tolerance of 0.95%. Based on the similarity of the control strains, isolates were considered clones if similarity was ≥ 88%. Salmonella serotype Braenderup strain H9812 was used as the standard. PFGE strain types were compared with USA types (100, 200, 300, 400, 500, 600, 700, 800, 1000, and 1100).
Statistical analyses. Descriptive statistics include the percentages of wastewater samples positive for MRSA (Table 1) and MSSA (Table 2) by WWTP. Because PFGE was not performed on all isolates, statistical analyses of antibiotic resistance data were limited to MRSA (n = 84) and MSSA (n = 58) isolates expressing unique phenotypic profiles; this allowed us to reduce bias that could be introduced by including clones. Two-sample tests of proportions were performed between MRSA and MSSA isolates with respect to the percent resistance of each group of isolates to each of the 18 tested antibiotics. Analysis of variance was then used to compare the average numbers of antibiotics against which MRSA and MSSA isolates were resistant. In all cases, p-values ≤ 0.05 were defined as statistically significant. All statistical analyses were performed using Stata/IC 10 (StataCorp LP, College Station, TX) and SAS 9.2 (SAS Institute Inc., Cary, NC).
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Publication 2012
Hydrostatic Filtration Dialysis (HFD): A schematic representation of the methodology used for vesicle isolation is shown in figure 1. Pooled urine samples (50 ml per tube) were centrifuged at a Relative Centrifugal Force (RCF) of 2,000 g calculated at average radius of 100 mm in a swing bucket rotor Benchtop Universal 320 centrifuge (Hettich Zentrifugen, Tuttingen, Germany) for 30 min at room temperature (RT) (without braking). The supernatant (SN) ~ 0.5l was poured in a separating funnel connected with a dialysis membrane made of cellulose ester (CE) with molecular weight cut-off (MWCO) of 1,000 kDa (Spectra/Por Biotech MWCO 1,000,000 MWCO Catalogue number 131486; Spectrum Laboratories, Ca) (Supplemental Fig. 1).
The hydrostatic pressure of the urinary solution in the funnel pushes the solvent (water) through the mesh of dialysis membrane (filtration), together with all the analytes below the selected MWCO. After the first step resulting in sample concentration, the separating funnel was refilled with 200 ml of deionised filtrate (0.22 µm) water (R ≥ 18.2 MΩ·cm, mQ water) to rinse away remaining analytes below the MWCO until the volume of 5–8 ml of volume is reached. This filtration-concentration-dialysis process is called “hydrostatic filtration dialysis(HFD).
HFD and differential centrifugation:The retained solution above the 1,000 kDa cut-off (HFDa) (5 ml) was then centrifuged at 5,000 g, 20,000 g and/or 40,000 g calculated at maximum radius 105 mm of a fixed angle JA-20 rotor (clearing factor or k factor = 770) (Beckman Coulter, Fullerton, Ca) for 1 h at RT. The retained 40,000 g supernatant (SN) fraction (5 ml) was then ultracentrifuged at 200,000 g calculated at maximum radius 91.9 mm of 70 Ti fixed-angle rotor (k factor = 44) (Beckman Coulter) for 2 h (RT) using a Beckman XL-80 Ultracentrifuge (Beckman Coulter). All the pellets were re-suspended in mQ water. For a pilot study, HFDa from the starting urinary volumes of 15, 50, 100 and 200 ml were concentrated to 3 ml. After determining the protein concentration, an equal amount of total protein was loaded in polycarbonate centrifugation tubes (3 ml). Ultracentrifugation was performed at 200,000 g calculated at the maximum radius 82.0 mm of 70.1Ti fixed-angle rotor (k factor = 36) (Beckman Coulter) for 2 h at RT.
Differential centrifugation and HFD: Comparative analysis was performed according to Fernández-Llama and colleagues15 (link). Pellets from 2,000 g and 17,000 g were resuspended in 10 ml of 250 mM sucrose, 10 mM triethanolamine pH7.6 and 200 mg/ml of DTT for 10 minutes at 37°C vortexing every 2 minutes. Centrifugations at 17,000 g (42 ml per tube of urine and 10 ml of dithiothreitol (DTT) fraction) were performed in a fixed angle JA-20 rotor (clearing factor or k factor = 770) (Beckman Coulter) for 30 min at RT. RCF were calculated at average radius of 70 mm. Ultracentrifugations (16,5 ml urine per tube and 10 ml of DTT fraction) were performed at 200,000 g calculated at maximum radius 91.9 mm of 70 Ti fixed-angle rotor (k factor = 44) (Beckman Coulter) for 2 h (RT) using a Beckman XL-80 Ultracentrifuge (Beckman Coulter). All the final pellets were resuspended in 1 ml of purified water. The final SNs were poured in HFD system and processed as described above. Conversely, the urine solution below the 1,000 kDa cut-off (HFDb) was ultracentrifuged (16.5 ml per tube) at 200,000 g calculated at maximum radius 91.9 mm of 70 Ti fixed-angle rotor (k factor = 44) (Beckman Coulter) for 2 h (RT) using a Beckman XL-80 Ultracentrifuge (Beckman Coulter).
Publication 2014
Cellulose Centrifugation Dialysis Dithiothreitol Esters Filtration G Force Hydrostatic Pressure isolation JA 20 Llamas Pellets, Drug polycarbonate Proteins Radius Solvents Sucrose Tissue, Membrane triethanolamine Ultracentrifugation Urine

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Publication 2020
Twenty-one water samples were collected in the Kattegat, the Baltic Proper and the Gulf of Bothnia using a FerryBox system installed in the ship TransPaper during 13th–19th of July 2013. The ship followed the route: Gothenburg (Sweden)—Kemi (Finland)—Oulu (Finland)—Lübeck (Germany)—Gothenburg. The FerryBox system consists of a pump with a water inlet at 3 m depth, a circuit of multiple sensors for temperature, conductivity, chlorophyll and phycocyanin fluorescence, turbidity, and oxygen as well as automated water sampling devices. A detailed description of the FerryBox system is found in Karlson et al. (in press ). Manual water sampling for DNA analysis was carried out both on the Northward and Southward legs. Approximately, 10 L of seawater were collected in a polycarbonate carboy. Subsamples of 200–500 mL were filtered onto 0.22 μm pore-size mixed cellulose ester membrane filters (Merck Millipore co., Cat. No. GSWP04700) to capture plankton. The filters were frozen in liquid nitrogen on board and kept at −20 to −80°C until DNA extraction.
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Publication 2016
cellulose ester membrane Chlorophyll Electric Conductivity Fluorescence Freezing Leg Medical Devices Nitrogen Oxygen Phycocyanin Plankton polycarbonate Strains
With fVi avMW 43 kDa, the following procedure was used to prepare conjugates. Polysaccharide was solubilized in 100 mM MES pH 6 at a concentration of 50 mg/mL. NHS and then EDAC were added to have 0.33 M NHS and EDAC/Vi repeating units molar ratio of 5. After the reaction was mixed at room temperature for 1h, the protein previously derivatized with ADH [10 (link), 21 (link)], was added to give a Vi concentration of 7.8 mg/mL in 20 mM MES, pH 6 and mixed at room temperature for 2h. For full length Vi, the PS concentration in the EDAC/NHS activation step was reduced to 4.2 mg/mL and to 1.7–3.5 mg/mL in the conjugation step in order to avoid gel formation. Different ratios of Vi to protein were used: 1:1, 2:1 or 1:2 in weight.
Full-length Vi-CRM197 conjugates were purified by tangential flow filtration by using a 300k membrane (Sartocon Slice Cassette 200 cm2 PES). Twenty cycles of diafiltration against 1M NaCl 20 mM NaH2PO4 pH 7.2 and subsequently twenty cycles of diafiltration against 20 mM NaH2PO4 pH 7.2 (Pin 2.0 bar; Pout 0.2 bar; permeate flow rate = 30–33 mL/min) were performed. For full-length Vi-DT conjugate purification was performed with a 100k membrane (Hydrosart 200 cm2 in stabilized cellulose). Full-length Vi-TT conjugate and fVi conjugates were purified by size exclusion chromatography on a 1.6 cm x 60 cm Sephacryl S300 column or 1.6 cm x 60 cm Sephacryl S100 HR column respectively [GE Healthcare] eluted at 0.5 mL/min in PBS. Fractions at higher MW that did not overlap free PS and free protein run on the same column in the same conditions were collected.
Activated Vi (with EDAC/NHS) was not isolated before protein addition, but a fraction of the mixture was sampled in process and characterized for quantifying the % of activated Vi repeating units (molar ratio % of NHS/Vi repeating units). The sample was desalted by PD10 column (SephadexTM G-25M, GE Healthcare) against HCl 55 ppm and analyzed by ion pair HPLC-RP for NHS quantification and by HPAEC-PAD for Vi PS quantification. For quantification of NHS ester groups introduced on Vi PS, samples were eluted on a C18 column (Phenomenex, Gemini-NX 5 μ) with 80% 10 mM TBABr, 0.17% NH4OH, 20% ACN in isocratic condition with a flow rate of 1 mL/min. Eluent pH allowed ester-NHS groups hydrolysis and formation of N-hydroxysuccinimidate anion that was detected at 260 nm eluted as ion pair with TBA. Calibration curve was built using NHS as standard in the range 3–50 nmol/mL.
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Publication 2017

Most recents protocols related to «Cellulose ester membrane»

Mixed cellulose ester membrane-bottom plates (Millipore) were coated with rT2544 or anti-mouse total immunoglobulin overnight at 4 °C. Wells were blocked with 1% BSA and incubated for 2 h at 37 °C. Cells isolated from mesenteric lymph nodes (MLN), Peyer’s Patches (PP), and spleen of immunized mice was added to blocked wells for 5 h, followed by washing with PBST. The plate was incubated with enzyme-conjugated anti-mouse IgG and IgA (Southern Biotech) overnight at 4 °C and developed with substrate. The number of spots was counted separately for each well. In a separate experiment, IFN-γ (ELISpot set from BD Bioscience) and IL-17 (ELISpot kit from R&D) pre coated mixed cellulose ester membrane-bottom plates were incubated with cells isolated from Peyer’s Patches (PP) stimulated with rT2544 for 24 h. The plate was incubated with enzyme-conjugated anti-mouse IFN-γ and IL-17 antibodies and developed with substrate. The number of spots was counted separately for each well.
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Publication 2024
For the fabrication of GO and PEI-GO films, GO and PEI-GO suspensions were prepared in 10 mL of water at 5 mg mL−1, and the resulting suspensions were vacuum-assisted filtered with a cellulose ester (CE) membrane of 0.45 μm pore size, respectively. After the completion of the filtration, the GO and PEI-GO films were taken off from a CE membrane and dried in an oven at 60 °C for 12 h.
Publication 2024
To confirm whether incubation with EB can inhibit acid-fast bacteria contamination on membrane filters, we used GVPC agar plates supplemented with EB. GVPC agar plates containing 100 µg/mL of EB were prepared. Bathwater samples were examined; 50 mL of acid-phosphate buffer was added to 50 mL of bathwater. After 10 min, the bathwater-acid-phosphate buffer sample was filtered through a mixed cellulose ester membrane filter with a pore size of 0.45 µm (ADVANTEC, Tokyo, Japan) . After filtering the were filtered through a cellulose acetate membrane filter with pore size of 0.2 µm for sterilization. ETH was dissolved in ethanol. et al., 2004 ) at a concentration of 30 mg/mL (as ethambutol dihydrochloride) . Cell suspensions of L. pneumophila (10 3 CFU/mL) and Mycobacterium spp. (10 6 CFU/ mL) were mixed, and an equal volume of EB-acid-phosphate buffer was added. After 5 min, 0.2 mL of the mixture was inoculated on a GVPC agar plate (where the final concentration of EB in the agar plates was approximately 160 µg/mL) and incubated at 36℃ for 6 d. The agar plates were visually observed for the growth of Mycobacterium spp. and L. pneumophila, and the colonies were enumerated.
Publication 2024
A standard conjugation assay in E. coli was carried out as previously described [29 (link)]. Briefly, the donor VA585-22 and recipient E. coli K12-GmR strains were grown overnight in LB broth supplemented with meropenem and gentamicin, respectively. Conjugation was performed in a 0.22 μm sterile cellulose ester membrane filter (Merck, Germany) deposited over an LB agar plate, pouring a 1:1 ratio (50 µL) of donor and recipient strains. The plate with the filter was incubated for 3 h at 37ºC, and then half of the membrane was mixed with 3 mL of LB broth and vortexed briefly. Then, 100 µL of this suspension were plated onto LB-Gm-Mem and incubated at 37 °C overnight to select transconjugants (E. coli K12- GmR-MemR).
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Publication 2024
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For the evaluation of the procedure, two protocols were applied to confirm the analyzer's results, [23] (ISO 9308-1:2014) and [24] (ISO 7899-2:2014). The procedure was followed by passing 100 ml of seawater through a 0,45 um Mixed Cellulose Ester (Whatman, Maidstone, UK) membrane filter via vacuum pump. After filtration, the membrane was placed on CCA and SB plates, respectively. The dishes were incubated at 37°C for 16-18 hours for CCA plates and 48 hours SB plates. Then, the confirmation of the sample for E. faecalis, continued by incubation in Bile Aesculin Agar for two hours at 44°C. The results were assessed by calculating the number of 221 bacterial colonies on plates on a colony counter (CC-J3, Bioevopeak).
Publication 2024

Top products related to «Cellulose ester membrane»

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Cellulose ester membrane is a type of laboratory filtration equipment. It is a thin, porous membrane made from cellulose esters. The membrane is designed to separate and filter materials based on their size and molecular weight.
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Mixed cellulose ester membrane is a type of laboratory filtration material. It is composed of a combination of cellulose esters, such as cellulose acetate and cellulose nitrate. The membrane serves as a medium for filtration, separation, and sample preparation in various scientific and analytical applications.
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The mixed cellulose ester membrane filter is a versatile laboratory filtration product. It is composed of a combination of cellulose esters, providing a durable and reliable filtration medium. The membrane filter is designed to efficiently separate and retain particulates, microorganisms, and other suspended matter from liquid samples during various analytical and purification processes.
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The mixed cellulose ester membrane filter is a laboratory filtration device. It is composed of a blend of cellulose esters and designed to filter liquids and remove particulates from solutions.
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The Zetasizer Nano ZS90 is a dynamic light scattering (DLS) instrument designed for the measurement of particle size and zeta potential. It utilizes a 633 nm laser and a detection angle of 90 degrees to analyze the Brownian motion of particles in a sample. The instrument can measure particle sizes ranging from 0.3 nm to 10 μm and zeta potential values from -500 mV to +500 mV.
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Mixed cellulose ester membrane filters are a type of laboratory filtration equipment used to separate and isolate particles, cells, or other materials from liquid samples. These filters are made from a combination of cellulose esters and provide a consistent and reliable filtration performance.
Multiscreen HA mixed cellulose ester membrane plates are a type of lab equipment used for filtration and separation processes. The plates contain a mixed cellulose ester membrane that can be used for various applications, such as cell culture, protein purification, and sample preparation.
Alkaline Phosphatase-conjugated goat anti-mouse total Ig secondary Ab is a laboratory reagent used for the detection of mouse immunoglobulins (Ig) in various immunoassay applications. It contains alkaline phosphatase enzyme-labeled antibodies that bind to the constant regions of mouse Ig molecules, allowing for colorimetric or chemiluminescent detection.
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Fetal Bovine Serum (FBS) is a cell culture supplement derived from the blood of bovine fetuses. FBS provides a source of proteins, growth factors, and other components that support the growth and maintenance of various cell types in in vitro cell culture applications.
Cellulose mixed ester (CME) filter membranes are a type of laboratory equipment used for filtration purposes. These membranes are made from a combination of cellulose esters and provide a selective barrier to the passage of particles, molecules, or other materials in a solution or suspension. The core function of CME filter membranes is to facilitate the separation and purification of various substances during laboratory processes.

More about "Cellulose ester membrane"

Cellulose-based membranes, also known as cellulose ester membranes, are a class of semipermeable barriers composed of derivatized cellulose polymers.
These versatile membranes are widely used in a variety of applications, including filtration, dialysis, and drug delivery.
They offer high permeability, good mechanical strength, and the ability to selectively transport molecules based on size and charge.
Researchers studying these cellulose-derived membranes often face challenges in identifying the optimal protocols and products from the scientific literature.
PubCompare.ai can help streamline this process by leveraging AI-driven comparisons to enable more reproducible and accurate results in cellulose ester membrane research.
Cellulose ester membranes, such as mixed cellulose ester (MCE) membranes, are a type of cellulose-based membrane that are often used in filtration and separation applications.
These membranes are composed of a mixture of cellulose esters, such as cellulose acetate and cellulose nitrate, and offer a range of properties that make them useful in various research and industrial settings.
The Zetasizer Nano ZS90 is a commonly used instrument for characterizing the size and zeta potential of particles and molecules in solution, including those present in cellulose ester membrane samples.
This information can be valuable in understanding the performance and behavior of these membranes.
In addition to filtration and separation, cellulose ester membranes are also used in cell culture and biochemical assays.
For example, MultiScreen HA mixed cellulose ester membrane plates are often used in enzyme-linked immunosorbent assays (ELISAs) to capture and detect specific analytes, such as proteins or antibodies.
In these applications, the membranes provide a substrate for immobilizing the reagents and facilitating the desired reactions.
When working with cellulose ester membranes, researchers may also encounter the use of secondary antibodies, such as Alkaline Phosphatase-conjugated goat anti-mouse total Ig secondary Ab, which can be used to detect and quantify target proteins or other biomolecules.
The use of fetal bovine serum (FBS) is also common in cell culture and other biological applications involving cellulose ester membranes.
By understanding the various aspects of cellulose ester membranes, including their composition, properties, and applications, researchers can more effectively leverage these versatile materials in their studies and achieve more reliable and reproducible results with the help of tools like PubCompare.ai.