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Supelclean envi florisil

Manufactured by Merck Group
Sourced in United Kingdom, Germany

Supelclean ENVI-Florisil is a solid-phase extraction (SPE) sorbent used for the purification and concentration of a wide range of organic compounds from various sample matrices. It is a chemically modified magnesium silicate material that provides efficient cleanup and selective extraction of analytes.

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4 protocols using supelclean envi florisil

1

Multiresidue Analysis of Pesticides

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Fipronil, cypermethrin, and tebuconazole standards, surrogate standard delta-hexachlorocyclohexane (δ-HCH), and labeled internal standard phenanthrene-D10 were obtained from Sigma-Aldrich (purity >97%, USA) for use in this study. All employed solvents (n-hexane, acetone, and toluene) were of HPLC grade (J.T. Baker, Netherlands). Glass fiber filters (47 mm, pore size 1.6 µm, Whatman, England), Supelclean ENVI-Florisil (500 mg/3 mL, Sigma-Aldrich, USA) normal-phase cartridges, and activated carbon (Merck, Darmstadt, Germany) were used for solid-phase extraction. The general physicochemical properties of Fipronil, cypermethrin, and tebuconazole are given in Supplemental Table S1.
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2

Analytical Workflow for Designer Drugs

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The analysis was done according to the laboratory protocol and the protocols described by Vaiano et al. (9 (link), 10 (link)). Solid-phase extraction was performed using the Supelclean Envi Florisil and Supelclean LC-18 for reversed-phase extraction (Supelco, Sigma Aldrich, Taufkirchen, Germany). For liquid-liquid extraction we used TOXI Tubes A (Varian, Palo Alto, CA, USA). Drugs were qualitatively analysed with a Shimadzu GC/MS-QP2010 Ultra (Shimadzu, Kyoto, Japan) gas chromatograph with mass spectrometer using the full-scan mode (m/z range 40–600). The chromatographic column was InterCap 5MS/NP (5 % phenyl-95 % methyl polysiloxane, length 30 m, diameter 0.25 mm, film thickness 0.25 μm). The initial column temperature of 90 °C was held for 3 min, then increased to 270 °C at 15°C/min and held there for 5 min, and then increased to 320 °C at 15 °C/min and held there for 27 min. The total run time was 50.33 min. Ultra-pure grade helium was used as a carrier gas at the flow rate of about 1.5 mL/ min.
The obtained data were compared with the Wiley mass spectra library of designer drugs (DD2015), the SWGDRUG free database, and our own in-house library containing about 1000 compounds and metabolites (11 , 12 ). Each sample was analysed twice.
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3

Targeted Analysis of Organic Contaminants in Dust

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Half of the dust extract volume was used for targeted chemical analysis of 124 organic contaminants. Following concentration using a SpeedVac™ Concentrator, samples were purified as described previously (Van den Eede et al., 2012 (link)). Briefly, samples were purified using solid phase extraction with Florisil cartridges (Supel-clean ENVI-Florisil, 6 mL, 500 mg; Supelco) as described previously (Van den Eede et al., 2012 (link)). Purified extracts were eluted in three fractions: 6 mL hexane (F1), 10 mL ethyl acetate (F2), and 6 mL methanol (F3). Fractions were concentrated to approximately 1 mL using a SpeedVac™ concentrator and F2 fractions were reconstituted in hexane prior to analysis. Concentrations of 124 chemicals were measured in indoor house dust extracts via LC-MS/MS and GC/MS. Briefly, F1 fractions were analyzed for PAHs, PCBs, PBDEs and other BFRs (Stapleton et al., 2014 (link)), and phthalates (Hammel et al., 2019 (link)), F2 fractions were analyzed for pesticides (Cooper et al., 2019 ) and OPFRs (Phillips et al., 2018 (link)), and F3 fractions were analyzed for PFAS, phenols, and parabens as described previously (Supplemental Methods, Table S2).
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4

Extraction and Analysis of Hand Wipe Samples

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Hand wipes were extracted and analyzed similar to methods developed by Van den Eede at al. (2012) (link). Wipes were spiked with the following internal standards: d15-tris(1,3-dichloro-2-propyl) phosphate (d15-TDCIPP; 45.6 ng) and 13C-triphenyl phosphate (13C-TPHP; 38.0 ng). Hand wipes were extracted in 1:1 dichloromethane:hexane (v/v) by sonication, and extracts were concentrated to ~1 mL using a SpeedVac™ Concentrator. Extracts were cleaned using Florisil® solid-phase extraction cartridges (Supel-clean ENVI-Florisil, 6 mL, 500 mg; Supelco), eluting the F2 fraction containing OPEs with 10 mL ethyl acetate. F1 fractions eluted using 6 mL hexane and F3 fractions eluted using 6 mL methanol were also collected and used for analyses not described in this paper. F2 fractions were concentrated to ~1 mL using a SpeedVac™ concentrator and were reconstituted in hexane prior to GC/MS analysis. Recovery of internal standards was assessed using d9-tris(2-chloroethyl) phosphate (d9-TCEP; 164.8 ng) for d15-TDCIPP, and d15-triphenyl phosphate (d15-TPHP; 164.8 ng) for 13C-TPHP. Field blanks (n=14) were analyzed in each batch for quality assurance and quality control (Table S2).
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