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Sterile centrifuge tubes

Manufactured by Corning
Sourced in United States

Sterile centrifuge tubes are laboratory equipment used for the separation and containment of liquids and solids through the process of centrifugation. These tubes are designed to withstand the forces generated during the centrifugation process while maintaining a sterile environment for the samples.

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5 protocols using sterile centrifuge tubes

1

Isolation of Echinococcus Protoscoleces

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Fresh livers of sheep naturally infected with E. granulosus were collected from a slaughterhouse in Urumqi, Xinjiang, China. The contents of the noncalcified, noninfected, intact unicystic E. granulosus vesicles were aseptically extracted from the livers of sheep infected. The contents were transferred to sterile centrifuge tubes (CORNING), centrifuged at 1500g for 10 min to extract the supernatant, which was then treated with endotoxin removal, and filtered through a 0.22 μm membrane (Millipore) and quantified for protein concentration before being frozen at −80°C. To naturally eliminate fragments of the brood capsule from the protoscoleces sediment, it was digested with 1% pepsin (BioFroxx) and then rinsed three times with sterile PBS containing 100 U/mL penicillin‐streptomycin solution (Gibco). The sediment was stained with 0.5% eosin (BKMAMLAB) for 5 min, and the number of active protoscoleces (>90%) was counted microscopically and diluted to 10,000 protoplasts/mL in suspension with sterile PBS containing penicillin‐streptomycin solution and kept on standby.11
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2

Characterization of Abandoned Pb/Zn Tailing Wetland

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The study site was selected in an abandoned Pb/Zn tailing wetland (24.382116° N, 116.213768° E) in Meizhou, Guangdong Province, China, which has been detailed in previous studies [1 (link), 45 (link), 46 (link)]. Samples of biological aqua crust (BAC) and source tailings together with unstable physical crust were collected from a tailing wetland [1 (link)]. Five replicate samples were collected from three sites, i.e. source tailings (control, C1–5, B0 group), upstream BAC (UB1–5, B1 group) and downstream BAC (DB1-5, B2 group) (Table S2). Samples were collected in Petri dishes (ϕ 9 cm, Corning, USA) for geochemical analysis and characterization and in sterile centrifuge tubes (50 mL, Corning, USA) for microbial analysis. Samples for molecular analysis were immediately transported at -18 °C to the laboratory, and then were stored at -80 °C until further processing.
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3

Isolation of Human Granulosa Cells

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Follicle fluid from large follicles with diameters > 14 mm was collected in 50 mL sterile centrifuge tubes (Corning, NY, USA) through transvaginal aspiration. The follicle fluid was centrifuged at 1500 rpm for 10 min, and the cell precipitates were resuspended in phosphate buffer saline (PBS) (HyClone, Chicago, USA), transferred onto the surface of the lymphocyte separation medium (GE healthcare, Sweden) and then centrifuged at 2000 rpm for 20 min. The hGCs in the interface layer were collected and washed with PBS. The follicle fluid from multiple follicles were pooled prior to collect the hGCs from the same patients at one time. The human granulosa cells were identified by detection of the marker FSHR using immunocytochemistry and the proportion of cells staining positive for FSHR is > 90% (Supplementary Fig. 1). The hGCs were snap-frozen and stored at -80 ℃ for further research.
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4

Isolating Larvae from Centrifuged Fluid

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To harvest the larvae the roll of paper was carefully removed and discarded from each tube. The remaining fluid containing the larvae was then combined into 50 ml sterile centrifuge tubes (Corning, New York, USA) and centrifuged at 2000 g for 5 min with the brake off. Forty-five milliliters of supernatant was then discarded and the larvae were resuspended in sterile water. This washing process was performed three times before resuspension of the larvae in 2 ml of sterile water in a 15-ml conical tube. Larval yields were calculated by examining the number of larvae in 5 × 20 µl aliquots of resuspended larval solution at × 40 magnification.
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5

Antarctic Soil Sampling Protocol

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Between October and November 2011, soil samples were collected from Bird Island (54.0089°S, 38.0662°W), Signy Island (60.7107°S, 45.5849°W) and Léonie Island (67.5984°S, 68.3561°W) in the sub‐Antarctic, low maritime and high maritime Antarctic respectively. In order to achieve consistency between islands, soil was collected from under populations of co‐occurring Deschampsia antarctica Desv. and Colobanthus quitensis (Kunth) Bartl., the only two native vascular plant species that occur in Antarctica. On each island, 50 ml sterile centrifuge tubes (Corning Inc, Corning, NY, USA) were used to collect soil samples by hammering them directly into the vertical walls of three pits at three depths (2, 4 and 8 cm). Thus, a total of 27 soil samples were collected from across the three islands. The three pits were a maximum of 1 km apart on each island, with an average distance of 311 m separating them. The soil, kept on ice after collection and frozen at −80 °C within 5 h, was freeze dried to preserve fungal nucleotides.
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