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4 protocols using benzo e pyrene

1

Comprehensive PAH Standard Solution Analysis

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A composite standard solution of 18 PAHs including acenaphthene(ANA), acenaphthylene (ANY), benzo(b)fluoranthene (BbF), benzo(k)fluoranthene (BkF), benzo(g,h,i)perylene (BPE), chrysene (CHR), fluoranthene (FLT), fluorene (FLU), naphthalene (NAP), phenanthrene (PHE), anthracene (ANT), benzo(a)- anthracene (BEA), benzo(j)fluoranthene (BjF), benzo(a)pyrene (BaP), benzo(e)pyrene (BeP), bibenzo(a,h)anthracene (BaA), indeno(1,2,3-cd)pyrene (IPY) and pyrene (PYR) was purchased from Sigma-Aldrich (USA), each at a concentration of 1000 μg·mL−1. N-hexane and acetonitrile were obtained from Chongqing Xinyu Chemical Reagent Co., Ltd. (China), both with an analytical grade.
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2

Polycyclic Aromatic Hydrocarbons Quantification

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Individual standards of 2,3-Benzanthracene, 1,2-Benzanthracene, Triphenylene, Rubrene, Pentacene, 1,2:5,6-Dibenzanthracene, and 1,2,3,4-Dibenzanthracene were purchased from Fisher Scientific (Waltham, MA). Pyrene, Benzo(a)Pyrene, Benzo(e)Pyrene, and Perylene were obtained from Sigma Aldrich (St. Louis, MO). Chrysene was obtained from Ultra Scientific (North Kingstown, RI). All chemicals were used as received without further purification. Individual standards were diluted to a final concentration of 0.7 ng/ml in toluene (Fisher Scientific, Waltham, MA). The PAHs in Soil certified research material which contains 16 PAHs at concentrations of 100 ppb to 1 ppm was obtained from Research Technologies Corporation (SQC017, Laramie, WY). The PAH containing soil was processed using ultrasonic extraction according to EPA method 3550C. A Tuning Mix mass spectrometry standard (Tunemix, G2421A, Agilent Technologies, Santa Clara, CA) was used as a mass and mobility calibration standard. Details on the Tuning Mix structures (e.g., m/z = 322 Ko= 1.376 cm2V−1s−1, m/z = 622 Ko= 1.013 cm2V−1s−1, and m/z = 922 Ko= 0.835 cm2V−1s−1) and TIMS mobility calibration procedures can be found elsewhere.13 (link),14
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3

PAH Detection in Environmental Samples

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Analytical grade (99.9% pure) acetone and hexane are purchased from Merck Millipore (Massachusetts, USA). 18 PAH standard mixture solution (Acenaphthene (AcP), Acenaphthylene (AcPy), Anthracene (Ant), Benzo[a]Anthracene (BaA), Benzo[a]pyrene (BaP), Benzo[e]pyrene (BeP), Benzo[b]fluoranthene (BbFL), Benzo[g,h,i]perylene (BghiP), Benzo[j]fluoranthene (BjFL), Benzo[k]fluoranthene (BkFL), Chrysene (Chr), Dibenzo[a,h]Anthracene (DBA), Fluoranthene (FL), Fluorene (Flu), Indeno [1,2,3-cd]pyrene (InP), Naphthalene (NaP), Phenanthrene (Phe) and Pyrene (Pyr)) are obtained from Sigma–Aldrich (Missouri, USA). Powdered Benzo[e]pyrene-d12 (BeP-d12) perdeuterated internal standard is purchased from Sigma–Aldrich (Missouri, USA). 16 PAH internal standard mixture solution (1000 μg/mL in toluene) (AcP-d10, Acpy-d8, Ant-d10, BaA-d12, Bap-d12, BbFL-d12, BghiP-d12, BkFL-d12, Chr-d12, DBA-d14, Flu-d10, FL-d10, InP-d12, NaP-d8, Phe-d10, Pyr-d10) are from Chiron (Trondheim, Norway). Disposable Nylone filters (0.22 μm) are provided by Merck Millipore (Massachusetts, USA).
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Organic Compound Extraction from Water

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Detailed information on chemicals used for producing SBAC and extracting organic compounds from water are found elsewhere (Björklund and Li 2015, Gong 2013) . Water was purified with a Synergy UV Milli-Q system from Millipore. Standards of fluorene (FL), anthracene (ANT), pyrene (PYR), benzo[e]pyrene (BeP), 4-nonlyphenol (NP), dibutyl phthalate (DBP) and di(2-ethylhexyl) phthalate (DEHP) were purchased from Sigma-Aldrich, and 4-t-octylphenol (OP) from Fluka. 9-chloroanthracene and phenanthrene-d10, from Sigma-Aldrich, were used as internal standards. Stock solutions of the organic compounds, as well as internal and calibration standards of analytes, were prepared in toluene, and working standards for spiking water samples were prepared in acetone. All solutions were stored in amber glass bottles at -18°C.
The procedure to extract organic compounds from water and the instrumentation used for analysis are described in detail elsewhere (Björklund and Li 2015) and are summarized in the Supplementary Material.
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