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3rd meeting of young researchers at UP 1 - IJUP - Universidade do ...

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Determin<strong>at</strong>ion <strong>of</strong> en<strong>do</strong>crine-disrupting compounds in w<strong>at</strong>er by gas<br />

chrom<strong>at</strong>ography with mass spectrometric detection<br />

S. Rocha 1 , C. Pinho 1 , V.F. Domingues 2 , C. Mansilha 3,4 , P. Gameiro 1<br />

1 REQUIMTE, Faculdade de Ciências da <strong>Universidade</strong> <strong>do</strong> Porto, Porto, Portugal<br />

2 REQUIMTE, Instituto Superior de Engenharia <strong>do</strong> Porto, Porto, Portugal<br />

3 Instituto Nacional de Saúde Doutor Ricar<strong>do</strong> Jorge, Porto, Portugal<br />

4 REQUIMTE, <strong>Universidade</strong> <strong>do</strong> Porto, Portugal<br />

Chemical compounds such as bisphenol-A (BPA), estrone (E1), 17β-estradiol (E2) and 17βethinylestradiol<br />

(EE2) are classified as “en<strong>do</strong>crine-disrupting compounds” (EDCs), th<strong>at</strong> were<br />

defined by the European Commission as “exogenous substances th<strong>at</strong> cause adverse health<br />

effects in an intact organism, or its progeny, consequent to changes in en<strong>do</strong>crine function” [1] .<br />

The n<strong>at</strong>ural estrogens such as E1 and E2 are mainly derived from excreta <strong>of</strong> humans and<br />

livestock. EE2 is a synthetic steroid and is the most common used as contraceptive and in<br />

hormonal therapies. Environmental w<strong>at</strong>ers contamin<strong>at</strong>ion is due to large volumes <strong>of</strong> municipal,<br />

agricultural and industrial wastew<strong>at</strong>er discharges. Apart from these steroids, BPA have been<br />

mainly used for the production <strong>of</strong> epoxy resins and polycarbon<strong>at</strong>es and it is also considered a<br />

compound with estrogenic activity, with impact in environment and an incipient <strong>of</strong> concern in<br />

bottled w<strong>at</strong>ers [2] .<br />

The main objective <strong>of</strong> this work was to implement and valid<strong>at</strong>e a sensitive and selective<br />

metho<strong>do</strong>logy to detect and quantify 4 EDCs, simultaneously, in environmental w<strong>at</strong>er samples<br />

and bottled w<strong>at</strong>ers (analysis <strong>of</strong> BPA) using solid-phase extraction (SPE) and Gas<br />

Chrom<strong>at</strong>ography tandem Mass Spectrometry (GC-MS), after deriv<strong>at</strong>iz<strong>at</strong>ion with silyl<strong>at</strong>ion<br />

agent N-methyl-N-(trimethylsilyl)trifluoroacetamide (MSTFA) [2] . The GC-MS determin<strong>at</strong>ions<br />

were performed in parallel on a Thermo Polaris Q with an ion trap mass spectrophotometer and<br />

a temper<strong>at</strong>ure-programmable injector (PTV) and on a Shimadzu GCMS-QP2010 Plus with a<br />

single quadrupole mass spectrophotometer in injection splitless mode. Linear calibr<strong>at</strong>ion<br />

curves were obtained to the EDCs for concentr<strong>at</strong>ions ranging from 50 to 500 µg.L -1 .<br />

The SPE optimiz<strong>at</strong>ion was <strong>do</strong>ne using different cartridges such as Grace Pure Fast, Grace Pure<br />

Low, Str<strong>at</strong>a TM -X, Str<strong>at</strong>a TM SDB-L, LiChrolut ® RP-18 and LiChrolut ® EN/RP-18. All analytical<br />

calibr<strong>at</strong>ion curves, from direct injection <strong>of</strong> standard mixtures showed a coefficient correl<strong>at</strong>ion<br />

level (R) higher than 0.996. Instrumental quantific<strong>at</strong>ion limits for BPA, E1, E2 and EE2 were<br />

54.4, 42.6, 50.1 and 91.9 μg.L -1 for Thermo Polaris Q and 62.8, 117.6, 180.0 and 68.0 μg.L -1<br />

for Shimadzu GCMS-QP2010 Plus, respectively. SPE metho<strong>do</strong>logy shows recovery above<br />

90% for all cartridges tested. The results suggest th<strong>at</strong> with a single step <strong>of</strong> sample prepar<strong>at</strong>ion it<br />

is possible to achieve good recoveries for these four EDCs, allowing the analysis <strong>of</strong> different<br />

w<strong>at</strong>er m<strong>at</strong>rices.<br />

References:<br />

[1] Jeannot, R., Sabik, H., Sauvard, E., Dagnac, T. and Dohren<strong>do</strong>rf, K. (2002), Determin<strong>at</strong>ion <strong>of</strong><br />

en<strong>do</strong>crine-disrupting compounds in environmental samples using gas and liquid chrom<strong>at</strong>ography with<br />

mass spectrometry, Journal <strong>of</strong> Chrom<strong>at</strong>ography A, 974, 143-159.<br />

[2] Quintana, J.B., Carpinteiro J., Rodriguez, I., Lorenzo, R.A., Carro, A.M. and Cela, R. (2004),<br />

Determin<strong>at</strong>ion <strong>of</strong> n<strong>at</strong>ural and synthetic estrogens in w<strong>at</strong>er by gas chrom<strong>at</strong>ography with mass<br />

spectrometric detection, Journal <strong>of</strong> Chrom<strong>at</strong>ography A, 1024, 177-185.<br />

252 3 rd <strong>meeting</strong> <strong>of</strong> <strong>young</strong> <strong>researchers</strong> <strong>at</strong> <strong>UP</strong>

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