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25 protocols using n hexane

1

Extraction of Bioactive Aqueous Extract

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The bioactive extract, previously identified as the delipidated aqueous phase, was obtained as previously described [13 (link)]. Briefly, total biomass obtained from a 500 mL culture in BHI was submitted twice to fractionation with 200 mL n-hexane (Tedia, Fairfield, OH, USA). The hexane solution was then removed under vacuum, and the remaining aqueous residue was extracted twice (200 mL) using the following solvents in this order: dichloromethane, ethyl acetate, and butanol (Tedia, USA). The organic fractions were evaporated and tested for antibiofilm activities. The delipidated aqueous phase was filtered (Millipore 0.22 μm), tested, and named as the aqueous extract.
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2

Isolation and Characterization of Phenolic Compounds

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The compounds viz., catechin, epicatechin, gallocatechin, epigallocatechin, epigallocatechin gallate, epicatechin gallate, and procyanidin B2 were obtained from Sigma (St Louis, MO, USA). Cyanidin chloride and delphinidin chloride were purchased from Axxora Co. Ltd. (Lausanne, Switzerland). Benzyl mercaptan was obtained from Aladdin (Shanghai, China). HPLC grade methanol, acetonitrile, chloroform, dichloromethane, ethyl acetate, n-hexane, n-butanol, and acetic acid were procured from Tedia Co. Ltd. (Fairfield, OH, USA). The following materials and equipment were used for separation and chromatography: Sephadex LH-20 (GE Healthcare, Sweden); silica GF254 TLC sheet (5 × 20 cm; HeFei BoMei Biotechnology Co., Hefei, China); ordinary-phase silica gel column (silica gel H, 200–300 mesh; Anhui Liangchen Silicon Material Co. Ltd., Huoshan, China); and a Varian Prostar HPLC instrument, Model 325 (Varian, Mulgrave, Australia). 1H-NMR and 13C-NMR spectra were obtained on an AVANCE AV 400 (400/100 MHz) spectrometer (Bruker, Fallanden, Switzerland). 13C-NMR spectra were recorded at 150 MHz in acetone-d6/D2O mixture using a Varian Mercury-600 spectrometer (USA).
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3

Drotaverine Hydrochloride Controlled Release

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AlphaAmoun (Egypt) has kindly supplied Drotaverine hydrochloride (DRH) and the marketed product Spasmocure® tablets (60 mg). Acrylamide (AM), guar gum (GG), gelatin, pluronic f-127 (PF127), carboxymethylcellulose sodium salt (CMC) and polyvinyl alcohol (PVA) were procured from Sigma-Aldrich (USA). Acrylic acid (AA), N,N'-methylenebisAcrylamide (BIS), sodium tripolyphosphate (TPP) and sodium borate were procured from Alfa Aesar (Germany). Ammonium persulfate (APS), N,N,N,N tetramethylethylenediamine (TEMED) and sodium alginate (ALG) were delivered from Fischer (UK). Glutaraldehyde (GL) was purchased from Acros (Belgium). Chitosan (CS) was delivered from Marine (India). N-Hexane was purchased from Tedia (USA). All other reagents and chemicals used were of analytical reagent grade.
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4

Radix Bupleuri Cultivation Regions in China

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Forty-two batches of Radix Bupleuri samples that were cultivated for two years were collected during September and October in 2021 from different cultivation regions in China, including Sanyuan County (SY) in Shaanxi Province, Shouyang County (SA) and Qingyang City (QY) in Gansu Province, Xinjiang County (XJ) and Wanrong County (WR) in Shanxi Province, Chengde City (CD) in Hebei Province, and Wuzhong City (WZ) in Ningxia Province. Their botanical origins were all authenticated to Bupleurum chinense DC by Professor Shumin Wang of Changchun University of Chinese Medicine, China. Authentic standards of SSa, SSd, SSc, SSe, and SSf were purchased from Shanghai Yuanye Biological Technology Co., Ltd. (Shanghai, China). HPLC-grade methanol, acetonitrile, and n-hexane were acquired from Tedia Company, Inc. (Fairfield, CT, USA), while formic acid was purchased from Thermo Fisher Scientific (Waltham, MA, USA). Analytical grade methanol, ammonia, and n-butanol were bought from Beijing Chemical Industry Group Co, Ltd. (Beijing, China). Ultrapure water was prepared by Milli-Q water purification apparatus (Merck Millipore, Bedford, OH, USA).
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5

Quantitative Analysis of PAHs

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Major reagents included the mixed standard solution of 16 priority PAHs: Naphthalene (Nap), Acenaphthylene (Acy), Acenaphthene (Acp), Fluorene (FLR), Phenanthrene (PHE), Anthracene (Ant), Fluoranthene (FLT), Pyrene (PYR), Chrysene (CHR), Benzo [a] anthracene (BaA), benzo[k]fluoranthene (BkF), Benzo[a]pyrene (BaP), Benzo[b]fluoranthene (BbF), Dibenz[a,h]anthracene (DhA), Benzo[ghi]perylene (BgP), and Indeno[1,2,3,cd]pyrene (IcP). The mixed standard solution was purchased from AccuStandard Company, New Haven, CT, USA. Chromatography-grade n-hexane and dichloromethane as an extract and eluent of PAHs were purchased from TEDIA Company, Fairfield, OH, USA. The anhydrous Na2SO4 was purified and activated prior to analysis in a muffle furnace at 400 °C for 4 h. The internal standard compound, Philippine-d10, was purchased from the J & K Company (San Jose, CA, USA). The internal standard compound was a pure substance, and the contents of the measured components were determined by comparison. Copper powder and silica gel were purchased from the National Pharmaceutical Group (Beijing, China). All other chemicals were analytical grade.
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6

Chlorfenapyr and Tralopyril Analytical Standards

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Chlorfenapyr standards (98.6%) were purchased from Tan-Mo Technology Co., Ltd., Changzhou, China. Tralopyril standards (98.6%) were purchased from Dr. Ehrenstorfer GmbH, Germany. Sodium chloride (AR) was purchased from Sinopharm Chemical Reagent Co., Ltd., Shanghai, Chian. PSA and GCB were purchased from Tianjin Bonaijer Technology Co., Ltd., Tianjin, China. Anhydrous sodium sulfate (AR) was purchased from Shanghai Runjie Chemical Reagent Co., Ltd., Shanghai, China. Chromatographically pure n-hexane and acetonitrile were purchased from Tedia Co., Ltd., Fairfield, USA. The Chlorfenapyr standard and Tralopyril standard were dissolved in n-hexane and acetonitrile to prepare a stock solution with a concentration of 1000 mg/L, stored at 4 °C in the dark. Diluted to different concentrations when used.
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7

Extraction of Voacanga pinnata Bark

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Plant material and solvents V. pinnata bark was collected in November 2019 from a local plantation located in Gerik, Perak, Malaysia. The plant was purchased and authenticated from ETHNO Resources Sdn. Bhd. (846944-K) herbal company, Selangor Malaysia (http://ethnoherbs.net/). A voucher specimen (PHG-P-VP-302) was deposited in the herbarium of Pharmacognosy Department, Faculty of Pharmacy, Ain Shams University, Cairo, Egypt. n-Hexane was purchased from Tedia ® (Ohio, USA).
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8

Interfacial Polymerization of Polyamide Membranes

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PAN powder, used without purification, was given by Tong-Hwa Synthesis Fiber Co. Ltd. (Taipei, Taiwan). The monomers for interfacial polymerization were as follows: p-phenylenediamine, C6H4 (NH2)2 (PPD, Alfa Aesar, Heysham, Lacashire, UK); ethylenediamine, C2H4(NH2)2 (EDA, Alfa Aesar, Heysham, Lacashire, UK); 1,4-cyclohexanediamine, C6H14N2 (CHD, Tokyo Chemical Industry Co. Ltd., Tokyo, Japan); and trimesoyl chloride, C9H3Cl3O (TMC, Tokyo Chemical Industry Co. Ltd., Tokyo, Japan). N-methyl-2-pyrrolidone and n-Hexane were solvents of PAN and TMC, respectively, and were procured from Tedia Company Inc. (Fairfield, OH, USA). Salts (MgCl2, MgSO4, Na2SO4, and NaCl) were purchased from Sigma-Aldrich (Saint Louis, MO, USA). Two commercial membranes (NF90 and NF270) were bought from DuPont, Taiwan. Brilliant blue R, as dye, was provided by Tokyo Chemical Industry Co. Ltd. (Tokyo, Japan). The distilled water was laboratory-produced using a Lotun Technic machine (Lotun Technic Co. Ltd., New Taipei, Taiwan).
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9

Analysis of Rice Plant Volatiles

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Plant VOCs were collected with a closed loop dynamic headspace sampling system, similar to the method described by Sun et al.59 (link). One milliliter of n-Hexane (Tedia, USA) was applied to elute VOCs from absorbent traps and 1300 ng Nonyl acetate (Sigma, Switzerland) was added to each sample as an internal standard. VOCs emitted from the Xoo infected rice and control rice plants were collected for 24 h (16 h in light and 8 h in darkness) at room temperature; BPH-induced plant volatiles from rice plants (each rice plant was also infested with 15 gravid female adults for 24 h) were collected for 8 h in the light (20000 lx) as described by Lou et al.60 (link). Each treatment contained three to five biological replicates.
Gas chromatography–mass spectrometry (GC/MS) analyses of VOCs were performed on a QP-2010 GC/MS instrument (Shimadzu, Japan) equipped with an HP-5 MS fused-silica column (30 m × 0.25 mm × 0.25 μm). (Agilent Technologies, http://www.agilent.com). Helium (1 ml/min) was used as the carrier gas, and the initial oven temperature was 40 °C, held for 1 min, ramped at 8 °C min−1 to 300 °C held for 5 min. VOCs were identified by comparing their GC retention indices and MS spectra with those from the NIST11 library. The Retention index for each compound was determined using a series of straight chain alkanes (C7-C30) as standards.
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10

Quantification of Phthalate Esters in Environmental Samples

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Five PAE analytical standards (≥99.0%) of DMP, DEP, DiBP, DBP, and DEHP were purchased from Dr. Ehrenstorfer GmbH (Augsburg, Germany). Optima GC–MS grade toluene, acetonitrile, and n-hexane were purchased from Tedia Co., Inc. (Fairfield, OH, USA). Analytical grade sodium chloride and anhydrous ethanol were purchased from Sinopharm Chemical Reagent Co., Ltd. (Shanghai, China). Solid-phase extraction glass columns (CARB/NH2, 1000 mg/6 mL) were purchased from Dikma Technologies Inc. (Beijing, China).
To remove possible cross-contamination of PAEs, all glassware and chinaware used in the study were immersed in methanol overnight, rinsed with hexane, and dried at 140 °C for at least 4 h. Organic solvents were redistilled before being used. Sodium chloride was heated at 450 °C for 4 h in a muffle furnace and kept in sealed glass vials after cooling. For PAE analysis, a procedural blank and solvent blank were run with every batch of samples for quality assurance and quality control.
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