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1

Evaluating Weight Loss and pH Changes of Biomembranes in SBF

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The membranes were immersed in SBF to assess their weight loss (%) and pH change (n = 5/group/time point). The pH change from the baseline pH of the SBF was measured using the pH meter (SevenCompact, Mettler Toledo GmbH, Greifensee, Switzerland). Then, the 10 mm × 10 mm membrane specimens were immersed in 4 mL of SBF/tube in 50 mL centrifuge tubes (Corning, Merck KgaA, Darmstadt, Germany). The tubes were incubated at 37 °C, and the pH of the solution of each membrane was measured on days 1, 3, 7, 14, and 21. The control group consisted of a solution without membranes. To measure the weight loss, each membrane was weighed (Wd0) using an analytical balance (Satorius, Goettingen, Germany) before immersion in 4 mL of SBF/well in 12-well plates (Corning, Merck KgaA, Darmstadt, Germany). The membranes were incubated at 37 °C, and the SBF was added every 10 days to maintain a constant volume. To measure the weight loss on days 15, 30, 60, 90, and 120, the membranes were collected, rinsed with distilled water, and freeze-dried in a freeze dryer (LaboGene, Lillerød, Denmark) for 3 h. Their dry weights (Wdt) were measured, and their weight loss was calculated as:
The morphology of the membranes during the test was evaluated via SEM (n = 2/time point).
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2

Calcium Ion Release from Dental Materials

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Disc-shaped specimens (8.0 mm in diameter, 1.6 mm in thickness) were prepared using polyvinyl chloride molds (n = 6/group). The pastes were compacted into molds and then light-cured on both the top and bottom surfaces. The discs were placed on the bottom of glass scintillation vials with 10 mL of water, sealed, and stored at 37 °C, and the water was collected and renewed after 3 h and 1, 3, 7, 14, 21, and 28 days [1 (link)]. The pH and calcium ion of the medium were monitored using a pH probe (InLab Routine Pro, Mettler-Toledo, Schwerzenbach, Switzerland) and a calcium ion selective electrode (perfectION, Mettler-Toledo) connected to a pH/Ion meter (SevenCompact, Mettler-Toledo), respectively. To measure the released calcium ion, the solution was supplemented with ionic strength adjuster after the pH measurement.
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3

Evaluating Acid Production of S. mutans

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Acid production of S. mutans was evaluated by a glycolytic pH drop assay [17 ]. Briefly, the samples with different concentrations were added to bacterial suspension which was containing 1% glucose. After 24 h of cultivation, the pH of the cultures was determined using a pH meter (SevenCompact, Mettler Toledo). Before inoculation, the initial pH of the medium with samples was also determined.
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4

pH Monitoring During Microbial Growth

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To follow the development of the pH of the medium during cultivation, samples were taken from the outlet of the reactor and measured with a pH meter (Seven Compact, Mettler Toledo, Switzerland). As a reference, the pH of the fresh medium was determined. Samples were taken in duplicates.
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5

Soil Heavy Metal Analysis Protocol

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For various heavy metals measurements, the cadmium (Cd), chromium (Cr), lead (Pb), arsenic (As), copper (Cu), nickel (Ni) and cobalt (Co) were determined in this study. To measure the concentration of metals, 0.5 g soils from each sample were digested with a mixture of concentrated HCl–HNO3–HF–HClO4 on a hot plate15 (link),28 (link). First, a soil sample (0.5 g) was weighed and digested with 5 ml HCl on an electric hot plate at 190 °C until the solution was reduced to 3 ml. Second, approximately 5 ml HNO3, 5 ml HF, and 3 ml HClO4 were added to the solution and were digested until no black material remained. After cooling, the digestion solution was moved to a volumetric flask and was diluted to 50 ml. Finally, the digestion solution was filtered through a Millipore filter (0.45 μm), and then the concentration of heavy metals was analyzed by using inductively coupled mass spectrometry (ICP-MS, NexION 300X, Perkin Elmer, Melville, NY, USA). The quality control (reference material: GSB07-3272-2015 (ESS-5) and blank samples were generated. The recovery rates of Cd, Cr, Pb, As, Cu, Ni and Co in the reference material were 92%, 93%, 104%, 96%, 92%, 89% and 86%, respectively. The soil pH was also analyzed using a pH meter (Seven Compact, Mettler–Toledo, Greifensee, Switzerland) in 2.5:1 water/soil suspensions in this study.
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6

pH Stability of Hibiscus Dye Extract

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The pH of different concentrations of the dye extract (CM) of the calyces of H. sabdariffa and the pH stability were determined and followed for 1 month using a digital pH meter (Seven Compact, Mettler Toledo, USA). The pH of the samples was read and recorded at the beginning of every week until the 4th week.
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7

Characterization of Contaminated Paddy Soil

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Contaminated soil was collected from the surface horizon (0–20cm) of a paddy field near a smelter (26°15′28.49″N and 118°15′12.78″E) in Youxi County, central Fujian Province, China. The soil samples were air-dried, ground, passed through a 2-mm sieve, and then analyzed (Table 4). Soil pH was determined using a pH meter (SevenCompact; Mettler-Toledo, Greifensee, Switzerland) in 5:1 water/soil suspensions. Cation-exchange capacity (CEC) was determined using 1 M ammonium acetate buffered at pH 7.0. Soil organic matter was determined using the K2Cr2O7 wet oxidation method. Soil particle-size distribution (<2 mm fractions) was determined using the pipette method after hydrogen peroxide treatments33 .
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8

Measuring Total Soluble Solids and pH

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Total soluble solid contents (Brix) were carried out at 20°C using an Abbe refractometer (Bellingham Stanley Limit 60/70 Refractometer, UK). pH was obtained by directly measuring fruit‐based water kefir samples using a pH meter (Seven Compact, Mettler Toledo, USA) equipped with a glass electrode. pH measurement was done in duplicate, and the experiment was conducted in triplicate during fermentation.
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9

Water Quality Assessment in Northern Portugal

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All water samples were collected in Northern Portugal on the 6th of May, 2017, between 15 and 16 h. High tide was at 13.13 h and low tide at 19.16 h; however, a limited influence of seawater was expected as the samples were collected in the first 1 m of the water column. River water sample was collected from Lima river in Viana do Castelo (41°41′17.7′’ N 8°47′23.9′’ W), lake water sample from lake of São Pedro de Arcos in Ponte de Lima (41°45′52.5′’ N 8°38′13.60′’ W), and estuary water from Lima river near the mouth of the river (41°40′58.14′’ N 8°49′35.67′’ W). pH was measured using a benchtop pHmeter (SevenCompact, Mettler Toledo) with an accuracy of ± 0.002. All other physical-chemical parameters of water were measured using the Sera Aqua-Test (Table S1).
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10

Rapid Airway Surface pH Measurement

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A sample ≥ 40 µL of the fluid and mucus mixture was obtained after 48 h treatment. To minimize the effect of the diffusion of carbonic dioxide, present in the cell incubator and plausibly in equilibrium with the fluid, ASL samples were rapidly collected in the incubator, and immediately measured (within 2 min) using a microelectrode (SevenCompact, Mettler-Toledo, Novate Milanese, Italy). The measurements were repeated at least in triplicate, discarding the discordant measurements.
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