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Ms105

Manufactured by Mettler Toledo
Sourced in United States, Switzerland

The MS105 is a high-precision analytical balance from Mettler Toledo. It offers a weighing capacity of up to 120 grams and a readability of 0.01 milligrams. The balance is designed for accurate mass measurements in various laboratory applications.

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Lab products found in correlation

3 protocols using ms105

1

Corrosion Rate and Viscosity Measurement

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After
the experiment, the corrosion products on the metal surface were removed
by pickling solution (deionized water, HCl, and hexamethylenetetramine).
An electronic balance (METTLER TOLEDO MS105) was used to weigh the
mass of coupons. The corrosion rate of metal was calculated according
to eq 8. where V is corrosion rate
(mm a–1), m is the weight difference
before and after corrosion (g), s is the area of
coupons immersed in solution (cm2), t is
the corrosion time (h), and d is the metal density
(g cm–3).
A viscometer (Brookfield) was used
to measure the viscosity of the system at different time nodes.
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2

Solubility of Bromine Flame Retardants

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Solubility, expressed as saturated concentration (cs, in mM), is the maximum concentration of a solute that can be dissolved in a solvent. cs of individual pure BFR in ScCO2 was measured gravimetrically using an analytical balance (MS105, Mettler-Toledo, USA) with a readability of 0.01 mg and calculated with the following equation: Since mass removal of BFR is not gravimetrically measurable in polymer samples, the Br content of polymer samples (CBr/polymer, in wt.%) before and after extraction were determined using an X-ray fluorescence analyzer (XRF) (Vanta C, Olympus, Japan) applying RoHS plus method. For this determination, the powdered polymer samples (200 mg) were pressed into a circular shaped disc using a hydraulic crimper (MSK-510M, MTI Co., China) at 160 °C and 5 MPa for 5 min. The mass removal of BFR in polymer matrix was calculated using the formula ∆(CBr/polymer•m)/CBr/BFR, where CBr/BFR is Br content in BFR compound (wt.%), only then the solubility can be calculated with Eq. (1) .All experimental data were displayed in a format of mean value ± standard deviation.
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3

PM2.5 Collection and Suspension Preparation

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PM2.5 was collected outdoors from November 2019 to February 2020. The average temperature and humidity during the sampling period are shown in Table 1. PM2.5 sampler (Dandong Better Instruments Co., Heilongjiang, China) was set at the Chinese Research Academy of Environmental Sciences, Beijing. The sampling flow rate was 16.67 L/min. PM2.5 was collected with Teflon membrane. Teflon membrane equilibrate in a constant temperature and humidity (20~25 °C, 50% humidity) box prior to this collection for 24 h, weigh the membrane with a 0.01 mg electronic scale (MS105 Mettler Toledo, Zurich, Switzerland) prior to sampling, weigh again after sampling, and record the difference in membrane weights. The collecting sampled membranes were stored at −20 °C until analysis. Each membrane is collected for 23 h (4:00 p.m. to 3:00 a.m. the next day).
The following is the process of PM2.5 suspension preparation. The Teflon membranes loaded with PM2.5 were ultrasonically extracted with ultrapure water. The mixture was then freeze-dried, and the solids were accurately weighed using a one ten-thousandth balance. Finally, the solids were mixed with DMEM medium without serum to form PM2.5 suspension. PM2.5 suspension was stored at 4 °C and protected from light before use.
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