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13 protocols using phs 25

1

Tahini-based Antimicrobial Formulations

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Tahini (fat 52.6%, protein 26% and carbohydrate 15.7%) was used in this study and the indigenous microbiota in tahini was less than 102 CFU/g, which did not interfere with the count of Salmonella cells grown on TSA. Diluted tahini (50% w/w) was prepared by adding sterilized water, simulating common edible methods at home or restaurant in the Chinese diet [6 (link)].
Essential oils (EOs, Jiangxi Global Natural Spice Co., Ltd., Jiangxi, China) including oregano, cinnamon, thyme, tea tree, eucalyptus, peppermint, garlic and turmeric oils were directly added into undiluted and diluted tahini, obtaining the concentration of 1–3%. ε-PL (BioDuly, Nanjing, China), tea-polyphenol (Macklin, Shanghai, China) and citric acid (CA, Huada, Guangdong, China) were dissolved or diluted to reach appropriate concentrations using sterilized water before adding to samples, obtaining the final concentration of 0.05–0.5% for organic acid and 0.05–0.4% for ε-PL or tea-polyphenol. The pH values of samples were measured at room temperature using a pH meter (PHS-25; INESA, Shanghai, China).
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2

Mg2+ Release and pH Analysis

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For Mg2+ release and pH analysis, 100 μl of solution was removed at the indicated time points and the ion concentration of magnesium (Mg2+) measured with an atomic absorption spectrophotometer (ContrAA700; Analytik Jena, Jena, Germany) and the pH value of the medium measured using a pH meter (PHS-25; INESA, Shanghai, China).
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3

Characterization of Novel Materials

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A six-speed viscometer
(ZDN-1), medium-temperature and -pressure filtration loss tester,
high-pressure/high-temperature instrument (GGS71-B), high-speed mixer
(GJD-B12K) and roller heater (XGRL-4A), and extreme pressure lubricator
were purchased from Chuangmeng instrument technology service Co. Ltd,
Tsingtao city. An ultrafine machine crusher (800Y) was manufactured
by Shanghai Machinery Factory. Omni Nano Brook 90 Plus particle size
analyzer was manufactured by Brookhaven Instruments Corp. The pH meter
(PHS-25) was manufactured by INESA Scientific Instrument Co. Ltd.
The freeze dryer was manufactured by Shanghai naai precision instrument
Co. Ltd. Scanning electron microscopes (ZEISS sigma300) were manufactured
by ZEISS Co. Ltd. The thermogravimetric analyzer (TG209-F3) was manufactured
by NETZSCH Co. Ltd. The laser particle size analyzer (Bettersize 2000)
was manufactured by Bettersize Co. Ltd.
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4

Characterization of SU-8 Microstructures

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SEM images were acquired by using a field emission SEM (JSM-7500F, JEOL), and the samples needed to be coated with a gold film (a thickness of ~3–5 nm) beforehand. The optical microscopy images were obtained using a Motic BA400 microscope equipped with a charge coupled device camera. The pH of the solutions was calibrated by using a precision pH meter PHS-25 (INESA) with a resolution of 0.01. The Young’s modulus of the SU-8 microstructures was measured by using an Agilent Nano Indenter G200 equipped with an XP-style actuator, and the continuous stiffness measurement method was adopted. The measurement was carried out using a Berkovich diamond tip at 30 °C with a relative humidity of 20%.
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5

Preparation of Acid Rain and Salt Solutions

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A distillation machine prepared the distilled water (Shenzhen Yiliyuan Water Treatment Equipment Co., LTD., Shenzhen, China). The main components of acid rain are NH4+, Ca+, Na+, K+, Mg+, H+, SO42−, HSO42−, NO3, HCO3, Cl, etc. The concentration of SO42 in acid rain is 5–10 times higher than that of NO3 . In this paper, the acid solution was prepared by analytically pure sulfuric acid and nitric acid and distilled water, according to SO42:NO3 = 9:1 and PH = 3 [28 (link),29 (link)], which is measured by PH-meter (PHS-25, Shanghai INESA Scientific Instrument Co., Ltd., Shanghai, China). Sodium chloride crystals and distilled water at a concentration of 7% prepared the salt solution. Figure 1 shows the distilled water and two solutions.
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6

pH Effects on Heavy Metal Adsorption

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The effect of pH on the removal of Cu(ii), Zn(ii) or Pb(ii) was performed by mixing 1 g L−1 of the as-prepared adsorbent with 50.0 mL of 200 mg L−1 metal solution with the pH range from 2.0 to 6.0 in a 150 mL Erlenmeyer flask. The pH value of the solution was measured by a pH meter (PHS-25, INESA, China). These samples were shaken in a thermostatic shaker at 130 rpm for 8 h at room temperature (i.e., 25 ± 1 °C), then the solutions were filtered and the residual concentration of heavy metal ions in the solution (Ce, mg metal per L) was determined using an Inductively Coupled Plasma Optical Emission Spectrometer (ICP-OES, Optima 8000DV, PerkinElmer, USA). All the experimental data were the average of the triplicate determinations. The equilibrium adsorption capacity (qe, mg g−1) and removal rate (R%) were calculated as follows: where C0 and Ce represent the initial and equilibrium metal ion concentrations of Cu(ii), Zn(ii) or Pb(ii) (mg L−1), respectively; V0 is the volume of the solutions used (L) and m is the amount (g) of adsorbents.
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7

Soil Chemical Characterization Protocol

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Water content, total organic carbon (TOC, dissolved), total nitrogen (TN), total sulfur (TS), total organic sulfur (TOS), and pH of the samples were determined. Briefly, the samples were dried at 105°C to determine the moisture. Any animal and plant residues, and stones were removed after drying. The samples were ground and passed through a 2-mm sieve. Then, the samples were mixed with DI water at a sample-to-water ratio of 1:5 (w/v) with continuous mixing for 4 h, and filtered with membrane filters (0.45 μm, F513132, Sangon Biotech Co. Ltd) prior to TOC and TN analyses (TOC-L TNM-L CSN, Shimadzu, Japan) (Jones and Willett, 2006 (link); Li et al., 2017 (link)). TS and TOS were measured using an automatic sulfur meter (CTS3000, Xuzhou Terui Instrument and Equipment Co., Ltd., Xuzhou, China) (Lange and Brumsack, 1977 (link); Bohn et al., 2002 ). Sample pH was determined with a soil-to-water ratio of 1:2.5 (w/v) using a pH meter (PHS-25, Shanghai INESA Scientific Instrument Co., Ltd., Shanghai, China) (Liang et al., 2017 (link)).
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8

pH Monitoring of Lignin Solutions

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The initial and final pH readings of the lignin media, and the initial and final pH of the chemically pretreated lignin solution with H2O2 were conducted with a pH meter (INESA, PHS-25, China) with a precision of 0.01. Intermediate readings were made with litmus paper. For litmus paper readings, a pH band of ±0.50 was added throughout the readings.
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9

Fermentation Analysis of NF and BMF

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The pH, reducing sugar, nitrite, and salinity of both NF and BMF samples after 10, 30, 60, and 90 days of fermentation were determined. Reducing sugar and nitrite were measured according to Chinese national standards (GB 5009.7-2016 and GB 5009.33-2016). pH of the samples was measured on a pH meter (PHS25, INESA, Shanghai, China), and their salinity was determined by a salinity meter (ES-421, ATAGO, Tokyo, Japan).
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10

Characterization of Degraded SMX Compounds

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SMX was measured using a high-performance liquid chromatography instrument consisting of a Sapphiresil C18 HPLC pump (150 mm × 4.6 mm, 5 μm, FULI, China) and a UV/visible detector (detection wavelength 264 nm). The degradation intermediates and debris ions of SMX over a certain period of time were determined by high-performance liquid chromatography mass spectrometry (Waters 2695 HPLC, WatersZQ 2000 MS, USA). The pH value of the reaction solution was measured or monitored using a pH probe (PHS-25, INESA, China). The MnO2 materials were characterized by scanning electron microscopy (SEM, Thermo Scientific Apreo 2 SEM, USA). For the SEM and EDS observation of amorphous MnO2, a piece of nickel foam was soaked in the solution for several seconds to collect the particles. Detailed information on the sample detection methods and AMO characterization methods are presented in Text S1.
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