Hidrológiai Közlöny, 2015 (95. évfolyam)
2015 / 5-6. különszám - LVI. Hidrobiológus Napok előadásai
72 HIDROLÓGIAI KÖZLÖNY 2015. 95. ÉVF. 5-6. SZ. No Vízfolyás megnevezése Mintahely GPS koordináta DRO LNG PRG 1. Zala folyó Őriszentpéter N46.83666, E16.43392 1.85 (0.04) 3.40(0.45) 3.25 (0.59) 2. Zala folyó Zalalövő N46.85013, E16.62666 <LOQ <LOQ 2.74 (0.12) 4. Zala folyó Petőhenye N46.88008, El6.92030 <LOQ <LOQ 2.92 (0.33) 5. Zala folyó Zalabér N46.97823, El7.02623 <LOQ <LOQ 2.81 (0.25) 7. Zala folyó Balatonhídvég N46.63705, E17.18369 1.54(0.03) 1.29 (0.09) 10.17(1.17) 9. Denke patak Pankasz N46.83737, E16.49827 <LOQ <LOQ 1.47 (0.16) 10. Szentjakabi csatorna Felsőjánosfa N46.84740, E16.55136 <LOQ <LOQ 0.52 (0.04) 12. Szélvíz Zalaszentgyörgy N46.86587, E16.69467 <LOQ <LOQ 0.73 (0.14) 14. Felső-Válicka Zalaegerszeg N46.84334, E16.86976 <LOQ <LOQ 4.91 (0.24) 15. Sárvíz Zalaszentiván N46.89049, E16.89153 <LOQ <LOQ 4.41 (1.31) 21. Héviz-páhoki csatorna Alsópáhok N46.76038, E17.20494 1.62 (0.05) 1.26 (0.01) 2.28 (0.34) 20. Sári csatorna Marcali N46.58546, El7.44281 <LOQ 2.14(0.04) 1.38 (0.03) 22. Edericsi patak Balatonederics N46.80127, E17.38797 <LOQ 0.85 (0.07) <LOQ 27. Egervíz Szigliget N46.80661, E17.45916 <LOQ <LOQ 1.81 (0.03) 28. Egervíz Hegyesd N46.91531, E17.52500 <LOQ <LOQ 1.88(0.07) 29. Egervíz Monostorapáti N46.92733, El7.55878 <LOQ <LOQ 2.37(0.03) 31. Örvényesi-séd Örvényes N46.91394, E17.81708 <LOQ <LOQ 0.23 (0.02) 32. Aszófoi-séd Balatonfüred N46.93233, E17.85875 <LOQ <LOQ 1.00 (0.01) 37. Kéki patak Balatonalmádi N47.04098, El8.02046 <LOQ <LOQ 2.27 (0.10) 42. Boronkai patak Marcali-Boronka N46.58641, E17.44498 0.26(0.01) <LOQ 2.07 (0.01) 43. Imremajori csatorna Balatonfenyves N46.70956, E17.47938 4.30 (0.30) 2.45 (0.01) 13.67(0.31) 1. táblázat - Progestin pozitív mintahelyek a Balaton és a Zala vízgyűjtőn. A táblázat első négy oszlopa mutatja a mintahely számát (No), a vízfolyás és a mintahely megnevezését a GPS koordinátáikkal együtt. Az utolsó három oszlop az átlagos progestin koncentrációkat mutatja ng/L-ben. Zárójelben a S.E.M. értékek vannak feltüntetve. Detection of anthroponetic steroid contaminations in catchment area of Zala River and Lake Balaton by HPLCMS/MS method Z Pirger'“, G Maasz'“'3, P Takács,h, S Lovas'“, Z Zrínyi'“, R Svigruha2, A Takátsy3, L G-Tóth'c, P Avar' 1- MTA Centre for Ecological Research, Balaton Limnological Institute, a- Department of Experimental Zoology, NAP B Adaptive Neuroethology, b- Department of Hydrozoology, Fish and Bentos Research Group and c- Zooplankton and Perifhyton Theme Group, Tihany, H8237, Hungary; 2- Limnoecology Research Group, Department of Limnology, University of Pannónia, Veszprém, H-8200, Hungary; 3- Department of Analytical Biochemistry, Institute of Biochemistry and Medical Chemistry, University of Pécs, Pécs, H-7624, Hungary Abstract: Freshwaters, such as lakes and rivers, today are subject to controlled pollution. Steroid hormones are chemically very stable, highly lipophilic molecules and their biological properties have a strong impact on the endocrine regulation of invertebrate and vertebrate species. Steroids have estrogenic, androgenic and progestogenic influence and based on it, they could modify the normal physiological mechanisms of freshwater species by mimicking the effect of endogen steroids. In this study, we focused on synthetic progestins as they are the main active ingredients of contraceptive pharmaceuticals. Progestins have been shown to impair reproduction in fish, amphibians and mollusks at low ng/L concentrations. In our measurements, we focused the most frequent oral contraceptive substances, such as levonorgestrel (LNG), drospirenone (DRO) and progesterone (PRG). We developed and optimized a quick, sensitive and relative cheap liquid chromatographic - mass spectrometric method with solid phase extraction to measure the hormone levels. Using our sensitive method (LOQ 0.03-0.11 ng/L) we could also detect progestins even between 0.1 and 1 ng/L concentrations. Analyzing freshwater samples from Lake Balaton catchment area we found influents where the concentration of these hormones were 0.26-4.30 (DRO), 0.85-3.40 (LNG) and 0.23-13.67 (PRG) in ng/L. Out of 53 collecting places 21 contained measurable progestin levels, which clearly demonstrates the applicability of our method, legitimates toxicology experiments on effected species and indicates monitoring efforts. Keywords: levonorgestrel, drospirenone, progesterone, catchment area of Lake Balaton and Zala River, HPLC-MS/MS.