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12 protocols using 3 4 dichloroaniline

1

Enzymatic Degradation of Lignin Derivatives

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Laccase from Trametes versicolor (EC 1.10.3.2), lysing enzymes from Trichoderma harzianum, Calcofluor white stain, 4-hydroxy-3,5-dimethoxy-benzoic acid (syringic acid), 3,5-dimethoxy-4-hydroxybenzaldehyde (syringaldehyde), 4-chloroaniline, 2,5-dichloroaniline, 3,5-dichloroaniline, and 4-nitroaniline were obtained from Sigma Chemical Co. (St. Louis, MO, USA). 3-chloroaniline, 4-methoxyaniline, 3-methoxyaniline, 3,4-dichloroaniline, 2-chloroaniline, organic solvents, and salts were obtained from Merck (Hohenbrunn, Germany). 4-(trifluoromethyl)aniline was obtained from Santa Cruz Biotechnology (Finnell St, Dallas Tx).Agar was obtained from Difco Laboratories (Detroit, MI, USA).
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2

Synthesis of Functionalized Compounds

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Standards: isatine, benzoic acid, 2-nitrophenol, diphenylamine were purchased from POCH (Avantor Performance Materials Poland S.A.), 3,4-dichloroaniline, 2,4-dichloroaniline, benzophenone from MERCK, diphenylmethane from Koch-Light. 3,4-Dichloroacetanilide was synthesized from 3,4-dichloroaniline and acetic anhydride. All reagents and chemicals were analytical purity grade.
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3

Preparation of 3,4-DCA Seawater Solutions

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3,4-Dichloroaniline was purchased from Sigma-Aldrich (purity > 98 %). Natural sea water was initially collected through a sand filter from 70 m depth in the Trondheimsfjorden. To produce a stock solution, 3000 μg 3,4-DCA was added to 1 L of filtered (1 μm, Sterivex) sea water and stirred vigorously for 2 h at 20 °C. The solution was then left to equilibrate for 30 min before being diluted to 3 L filtered seawater to reach a nominal concentration of 1000 μg/L, which was used as the highest exposure concentration in the test. This solution was further diluted with filtered seawater to produce the other exposure solutions at nominally: 25, 50, 150, 250, and 500 and 1000 μg/L.
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4

Embryo Toxicity Assay for Insecticide Mixture

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A binary mixture of insecticide was tested for 5 (d-tetramethrin: 0.01 – 1.20 μmolL−1 and cyphenothrin: 0.02 – 3.20 μmolL−1) concentrations prepared as dilutions with standard dilution water. Thirty fertilized eggs were randomly selected and transferred into 60 mm petri dish containing different concentrations of binary mixture of d-tetramethrin and cyphenothrin that are used for the assay, the positive control (4 mgL−1 (24.69 μmolL−1) 3,4-dichloroaniline) [27 ] (Sigma, USA), and negative control (only dilution water) [27 ], respectively, to minimize the dilution of concentration from the transfer straight from dilution water and to minimize the delay in exposure.
Twenty embryos were individually exposed in 24-well microtiter plates (Corning, USA), each well containing 2 ml of the respective concentrations of a mixture of insecticide. Plates were pretreated with respective solutions to minimize the absorption of the plastic material [27 ]. A single 24-well plate was used for each concentration of test, negative control, and positive control. Twenty wells of each plate were used for test solution and the remaining 4 wells served as internal control (containing dilution water). The plates were covered with non-adhesive foil and kept at RT (26°C) away from direct sunlight for 24, 48, and 72 hrs [27 ]. Assays were initiated within 2 hrs of post-fertilization.
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5

Evaluation of Complex Petroleum Substance Toxicity

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Benzo[a]pyrene (BaP; CAS no. CAS No. 50–32–8), 5-fluorouracil (CAS no. 51–21-8) and 3,4-dichloroaniline (CAS no. 95–76-1) were purchased from Sigma-Aldrich (Zwijndrecht, The Netherlands). All stocks and dilutions of test compounds were prepared in dimethyl sulfoxide (DMSO) (Merck, Darmstadt, Germany).
DMSO extracts of the sixteen complex petroleum substances (Fig. 1) were tested, including a distillate (sample SN100-DIS, CAS No. 64741–50-0), an aromatic extract (sample SN100-AE, CAS No. 64742–05-8), waxy raffinates (samples SN100-WR and SN400-WR; CAS No. 64741–89-5), base oils (sample SN100-LBO, CAS. No 64742–65-0; sample SN500-LBO, CAS. No 64742–65-0; sample SN100-BO, CAS No. 64742–56-9), a technical white oil (sample SN100-TWO, CAS No. 8042–47-5), a medicinal white oil (sample SN100-MWO, CAS No. 8042–47-5), a slackwax (sample SN400-SW, CAS No.64742–61-6), a hard paraffin wax (sample SN400-HPW, CAS No. 8002–74-2), a highly refined hard paraffin wax (sample SN400-HPHPW, CAS No.64742–51-4), a waxy brightstock (sample WBS, CAS No. not available), a brightstock slackwax (sample BSSW, CAS No. not available), a microcrystalline wax (sample MCW, CAS No. 63231–60-7), and a hydrogenated microcrystalline wax (sample HGMCW, CAS No. 64742–60-5).
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6

Analytical Determination of Pesticides and Phthalates

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Analytical grade dimethyl phthalate, monomethyl phthalate, dibutyl phthalate, dioctyl phthalate, propanil, monalide, chlorpropham, carfentrazone-ethyl, methomyl, 3-chloroaniline, 4-chloroaniline, and 3,4-dichloroaniline were purchased from Sigma-Aldrich (Castle Hill, Australia). Sulfosulfuron, metsulfuron-methyl, pyrazosulfuron-ethyl, imazethpyr, and pendimethalin were gifted by Dow Agrosciences (India). All other chemicals were used at the highest purity available commercially.
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7

Solubilization of OTA and 3,4-Dichloroaniline

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All chemicals were obtained from Sigma-Aldrich (Buchs, Switzerland) unless indicated otherwise. The OTA (Sigma Cat. No. 01877; produced by Petromyces albertensi, lot No. 067M4011V) and 3,4-Dichloroaniline (Sigma Cat. No. 437778; lot No. 13509KQV) were solubilized in pure ethanol before use.
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8

Hapten-Based Competitive ELISA Protocol

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Bovine serum albumin (BSA), rabbit serum albumin (RSA), ovalbumin (OVA), 3,4‐dichloroaniline, atrazine desethyl (6‐Chloro‐N,N‐dimethyl‐1,3,5‐triazine‐2,4‐diamine), N‐(1‐naphthyl)‐ethylene‐diamine, 2‐benzimidazole propionic acid, aflatoxin‐BSA conjugate (hapten density of 8‐12), N‐hydroxysuccinimide (NHS) ester, O‐phenylenediamine dihydrochloride (OPD), 2‐(N‐morpholino) ethanesulfonic acid (MES), and dimethylformamide were purchased from Sigma‐Aldrich (St. Louis, MO). Goat anti‐human IgG+IgM+IgA‐HRP labeled Abs were purchased from Abcam (Cambridge, MA). Vacutainer tubes were obtained from BD Diagnostics (Franklin Lakes, NJ). EDC [1‐ethyl‐3‐(3‐dimethyl aminopropyl) carbodiimide] and Nunc maxiSorp flat‐bottom plates were purchased from Thermo Fisher Scientific (Waltham, MA). All the reagents and solvents were of analytical grade.
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9

Thiram and 3,4-dichloroaniline Toxicity Assay

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Thiram (98.4% purity) and 3,4-dichloroaniline (98% purity) were purchased from Sigma-Aldrich (St. Louis, MO, USA). Thiram stock solutions were prepared in dimethyl sulfoxide (DMSO) and stored at −20 °C for further use. Test solutions (40, 20, 10, 5, 2.5, 1.25, and 0.625 μg/L) were prepared by dissolving the required volume of stock solutions in E3 buffer (290 µg NaCl; 8.3 µg KCl; 48 µg CaCl2; 81.5 µg MgCl2 to each mL of deionized water and 0.1% methylene blue; pH 7.2). All the chemicals used in this investigation were purchased from Sigma-Aldrich (St. Louis, MO, USA) unless otherwise stated.
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10

Analytical Reagents for Glutathione S-Transferase Assay

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Nanopure water was obtained from Barnstead Nanopure, Fisher Scientific (United States).
Methanol and ethanol, for HPLC, gradient grade, ≥99.8% and formic acid were purchased from Fisher Scientific (United States). 3,4-dichloroaniline, 1-chloro-2,4-dinitrobenzene (CDNB), and 5-chloro-2,4-dinitrotoluene (CDNT) were purchased from Sigma Aldrich (United States). The Glutathione S-Transferase (GST) Assay Kit (CS0410) was purchased from Sigma Aldrich (United States).
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