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Ml204t

Manufactured by Mettler Toledo
Sourced in United States

The ML204T is an analytical balance from Mettler Toledo. It is designed to provide precise and accurate weighing measurements for laboratory applications. The balance features a high-resolution readability and a sturdy construction to ensure reliable performance.

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5 protocols using ml204t

1

Dissection and Preservation of Skeletal Muscles

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The tibialis anterior (TA) and gastrocnemius (GC) muscles were immediately dissected and washed in phosphate-buffered saline (PBS) after anesthesia. Then, excess PBS was removed by blotting on a paper towel and the muscles were weighed using an analytical scale (Mettler-Toledo International Inc., model# ML204T). For protein extraction, tissues were snap-frozen in liquid nitrogen and stored at −80 °C; for histology (hematoxylin and eosin (H&E) staining) and immunohistochemistry, tissues were fixed via overnight immersion in 10% phosphate-buffered formalin.
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2

Microwave-Assisted Elemental Analysis

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Samples and reagents were weighed using an analytical balance ML 204T (Mettler Toledo, Columbus, OH, USA). The microwave-assisted acid digestion was performed in 100 mL closed Teflon vessels using an ETHOS PLUS microwave lab-station (Milestone, Sorisole, Italy). The total metal content was assessed using a NexION® 300X ICP-MS (Perkin Elmer, Waltham, MA, USA) equipped with a SeaFastSC2 DX autosampler (Elemental Scientific, Omaha, NB, USA). The nebulisation system consisted of a Meinhard® nebuliser and a cyclonic spray chamber thermostated by a Peltier refrigerator.
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3

Membrane Water Uptake and Density Characterization

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Using a 19 mm diameter stainless-steel hole cutter, circular samples were cut from the prepared membrane films and equilibrated in DI water for at least 48 h. The samples were removed and lightly wiped to remove surface water, and their wet mass, Ws , was measured gravimetrically. Samples were then dried under a vacuum oven at 50 °C for at least 24 h prior to measuring their dry mass, Wd . Water uptake, ωw , was determined as follows: ωw=WsWdWd×100%
A density kit (ML-DNY-43, Mettler Toledo, Columbus, OH, USA) and scale (ML204T, Mettler Toledo) were used to measure the dry polymer density, ρp , as [23 (link),24 (link)]: ρp=ρwρ0WdWdWL+ρ0
where WL is the sample mass measured in the auxiliary liquid (DI water), ρw is the auxiliary liquid density at the measurement temperature (997.8 kg/cm3 at 22 °C), and ρ0 is the air density (1.225 kg/m3). By assuming the volume additivity of water and polymer [25 (link)], water uptake and density characteristics were used to calculate the water volume fraction, ϕw , in the polymer films.
ϕw=WsWd/ρwWsWd/ρw+Wd/ρp
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4

Gravimetric Water Uptake and Density Characterization

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Water uptake was measured gravimetrically. A 0.75-inch diameter hole-punch was used to cut each hydrated film. The mass of each hydrated film, Ws , was measured after quickly blotting them with tissue paper. The films were then dried under a vacuum at 50 °C for 24 h and the mass of each dried film, Wd , measured [29 (link)]. The water uptake, ωw , was calculated as follows: ωw=WsWdWd×100%
where Ws is the mass of the swollen film and Wd is the mass of the dried film.
Film density was measured by the buoyancy method with a density kit (ML-DNY-43, Mettler Toledo) coupled with a scale (ML204T, Mettler Toledo) [48 (link)]. The density, ρp, was calculated as follows: ρp=ρLρ0W0W0WL+ρ0
where ρL is the density of water (997.8 kg/m3 at 22 °C), ρ0 is the density of air (1.225 kg/m3), W0 is the weight of the dried film in air, and WL is the weight of the film in water.
Water volume fraction, ϕw, was calculated as follows: ϕw=WsWd/ρpWsWd/ρL+Wd/ρp
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5

Urban PM2.5 Sampling and Analysis

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PM2.5 sampling was conducted on the rooftop (~25 m high) of a 6-storey teaching building in Tianjin University, located at 39.11° N, 117.16° E in the center of Tianjin, which represents a typical urban environment (Figure 1) during the winter (domestic heating period) of three consecutive years, i.e., 2017, 2018, and 2019 (Table S1). PM2.5 samples collection membranes were pre-combusted when collected (450 °C for 6 h). Quartz filters (23 × 18 cm) using a high-volume air sampler (TE-PM2.5HVP-BL, TISCH, Cleves, OH, USA) at a flow rate of 1.05 m3 min−1 during 8:00–18:00 (local time) for daytime and from 18:00 to next morning 8:00 for nighttime in both the seasons, and stored at −20 °C. The membranes were weighed before and after sampling using a microelectronic balance (Mettler Toledo ML 204T, Switzerland) after a 48-h equilibration in a drying vessel. One blank filter was also collected in each campaign. The samples were classified into clean (PM2.5 ≤ 75 μg m−3) and polluted (PM2.5 > 75 μg m−3) periods based on the PM2.5 mass concentration. Temperature (T), relative humidity (RH), and wind speed (WS) were measured at sampling points using a meteorological station (Gill MetPak, Gill Instruments, Lymington, Hampshire, UK). Gaseous pollutant (O3, SO2 and NO2) concentrations collected from the Tianjin Air Quality Monitoring Station data, located 1.7 km away from the sampling site.
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