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172 protocols using bisphenol a

1

Isolation and Degradation of BPA-Degrading Bacteria

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Bisphenol A and ethyl acetate (HPLC grade) were obtained from Merck (Darmstadt, Germany). HPLC grade acetonitrile and ethanol were purchased from S. Witko - JT Baker (Lodz, Poland). Water used as a HPLC solvent was purified with a Direct-Q® Water Purification System (Merck). The standard stock solutions of BPA (7 g L− 1 or 5 mg 5 mL− 1) were prepared in 70% ethanol and stored at 4 °C up to three months. Final concentration of BPA and ethanol in medium were 100 mg L− 1 and 1% (v/v), respectively. Basal Salt Medium (BSM) (Badiefar et al. 2015 (link)) was used for isolation and purification of bacterial species and the degradation study. For bacteria isolation, BSM was supplemented with nystatin (4 g L− 1) and actidione (4 g L− 1) to inhibit the growth of fungi.
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2

Silane-Based Nanomaterial Synthesis

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Pyridine (Aldrich) was dried on molecular sieves of 3Å. The β-cyclodextrin (BCD-OH) (≥95.0%, Wacker Chemie) was vacuum dried before use for 24 h. Glucose (Aldrich anhydrous), phenol (Merck), sulfuric acid (Sigma-Aldrich, St. Louis, MO, USA), bisphenol A (Merck), ethanol (Chimopar), 3-(triethoxysilyl)propyl isocyanate, tetraethyl orthosilicate (TEOS) (Aldrich), cetyltrimethylammonium bromide (CTAB), and sodium hydroxide (Fluka) were used as received.
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3

Endocrine Disruption Assay Protocol

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Implants: cholesterol, bisphenol A (CAS number 80-05-7) and bisphenol S (CAS number 80-09-1) were purchased from Merck KGaA (Darmstadt, Germany). VTG ELISA: secondary antibodies including horseradish peroxidase kit were obtained from Bio-Rad (Hercules, CA, USA). RIA: T3, and T4 label were purchased from Perkin-Elmer (Waltham, MA, USA) and antibodies for T3 and T4 were obtained from In Vitro technologies (Melbourne, Australia).Giemsa was purchased from Titolchimica spa (Rovigo, Italy).
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4

Laccase Purification from P. variabile

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The produced laccase of P. variabile was purified from fungal culture broth based on the method described by Forootanfar et al.
[28 (link)] and applied in pollutant removal experiments. Phenol, bisPhenol A (BPA), and 4-aminoantipyrine (4-AAP) were purchased from Merck (Darmstadt, Germany). 2,2′-Azinobis-(3-ethylbenzthiazoline-6-sulphonate) (ABTS) was obtained from Sigma-Aldrich (St. Louis, MO, USA). All other chemicals were of analytical grade.
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5

Bisphenol A and Nattokinase Assay

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Bisphenol A (BPA) was purchased from Merck KGaA, Darmstadt, Germany, CAS Number: 80–05-7, Cat. No.: 803546. Nattokinase (NK) was purchased from Doctor’s Best (USA), Item Code: 286,737, UPC: 75,395,000,253.
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6

Purification and Functionalization of Monomers

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Styrene (ST) (Sigma-Aldrich, St. Louis, MO, USA) has been purified through vacuum distillation. 2-Hydroxyethyl methacrylate (HEMA) (Sigma-Aldrich, St. Louis, MO, USA) and glycidyl methacrylate (GMA) (Merck, Darmstadt, Germany) have been purified by passing over short columns of activated basic alumina. Potassium persulfate (K2S2O8) (KPS) (Merck, Darmstadt, Germany) has been recrystallized from an ethanol/water mixture and then vacuum-dried. β-cyclodextrin (BCD-OH) (≥95.0%, Wacker Chemie, Munich, Germany) was vacuum-dried before use for 24 h. p-Toluene sulfonyl chloride (Ts-Cl) (reagent grade, ≥98%, Merck, Darmstadt, Germany), sodium hydroxide (reagent grade, ≥98%, pellets (anhydrous), (Sigma-Aldrich, St. Louis, MO, USA), 1,4-Diaminobutane (99%, Sigma-Aldrich, St. Louis, MO, USA), acetone (for analysis, >99%, Chemical Company Iasi), dimethyl sulfoxide (DMSO) (Aldrich-anhydrous, Darmstadt, Germany), pyridine (Aldrich, Darmstadt, Germany), glucose (Aldrich anhydrous, Darmstadt, Germany), phenol (Merck, Darmstadt, Germany), sulfuric acid (Sigma-Aldrich, St. Louis, MO, USA), bisphenol A (Merck, Darmstadt, Germany), ethanol (Chimopar, Bucuresti, România) were used as received.
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7

Photocatalytic Degradation of Organic Pollutants

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The reactions were performed on a Heidolph MR Hei-Tec, equipped with Radleys Heat-On heating mantle. The solvents (dichloromethane, methanol, 99.5% of purity) were obtained from commercial suppliers (TCI, Zwijndrecht, Belgium) and used without further purification unless otherwise stated. The P25 Aeroxide titanium(IV) oxide was purchased from Sigma-Aldrich, Taufkirchen, Germany. The other reagents (bisphenol A, methylene blue, and carbamazepine) were purchased from Merck, Darmstadt, Germany; TCI, Zwijndrecht, Belgium; and Fluorochem, Glossop, UK.
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8

Daphnia magna Exposure to Bisphenol-A

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Cultures of D. magna were initiated from third brood Bham2 strain neonates and maintained at a density of 20 animals/L in borehole water (collected from the University of Birmingham). The cultures were held at 20 °C with a 16 h:8 h light:dark photocycle and fed daily with Chlorella vulgaris (100 µL/animal, 500 cells/µL) as previously reported [48 (link)]. Media changes were carried out three times per week during maintenance and daily during chemical exposures.
The single exposure concentration of bisphenol-A (>99%, Merck Life Science Ltd., Gillingham, Kent, UK) in this study was determined by conducting a range finding experiment using 0, 5, 8, 10, 12, and 20 mg/kg with each test vessel containing 500 µL/L of DMSO as a solvent carrier and a total of 8 biological replicates per concentration. Single daphnids in individual 80 mL vessels were exposed immediately after their 6th maternal brood (3–4 weeks old) with samples taken at 8, 24, 48, and 72 h.
For the sample set that was analysed in this work, three biological replicate samples were taken from the control animals and those that were exposed to a single BPA concentration of 5 mg/kg using the same protocol as described for the range finding.
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9

Bisphenol A Exposure Routes in Sheep

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Bisphenol A of ! 99% purity (Merck, Sigma-Aldrich, Darmstadt, Germany) was dissolved in absolute ethanol for the dietary route and in corn oil for the subcutaneous route of administration. The dosage administered to the sheep was adjusted to the body weight recorded on the day of the administration. For dietary administration BPA solution in absolute ethanol was spilled onto the pellet ration (on average 1.18 mL of solution on 50 g of pellets), and applied on the morning dosage of pellets (400 g). For subcutaneous administration, injection of BPA solution was performed in the shoulder area (2.9 mL). BPA solutions were stored in sealed amber glass bottles at the ambient temperature for the entire experiment. Solution preparation, sample processing and assays were performed with the materials either made of glass or of BPA-free plastics.
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10

Polyelectrolyte Multilayer Membranes

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The chemicals PSS (30 wt
% with Mw ∼ 200 kDa and 25 wt %
with Mw ∼ 1000 kDa), PDADMAC (20
wt %, Mw ∼ 200–350 kDa),
PEI (50 wt %, Mw ∼ 750 kDa), sodium
hydroxide (NaOH, >98%), sodium chloride (NaCl, >99.5%), hydrochloric
acid (HCl, 37%, ACS reagent), glutaraldehyde (GA, 50 wt %), glycerol
solution (86–89 wt %), MPD (99%), 1,3,5-benzenetricarbonyl
trichloride (98%, TMC), n-hexane (≥99%), magnesium
sulfate (MgSO4, >99.5%), sodium sulfate (Na2SO4, 99%), magnesium chloride hexahydrate (MgCl2.6H2O, ≥99%), sodium chloride (NaCl, >99.5%),
polyethylene
glycol (PEG) with different molecular weights (Mw 200, 400, 600, 1500, and 2000 g·mol–1), atrazine (analytical standard), atenolol (>98%), bezafibrate
(>98%),
bromothymol blue (>95%), bisphenol-A (>99%), naproxen (analytical
standard), phenolphthalein (analytical standard), and sulfamethoxazole
(analytical standard) were purchased from Merck (The Netherlands).
PAH (40 wt %, Mw ∼ 150 kDa) was
purchased from Nittobo Medical Co. Ltd., Japan. Deionized water was
obtained from a Milli-Q Ultrapure water purification system.
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