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AR226-3351 ES Bioconcentration Screening of Perfluorinated Compounds Using Fathead Minnows Hoke, R., Turner, J.T., Gibson, W.R., Good, R.M., Green, J.W., and Buck, R.C. posto Introduction Perfluorinated compounds have been the focusofincreasing scrutiny by regulatory agencies and the industries that manufacture these compounds. ETT - potential environmental persistence - potential bioconcentration in fish An initial screening evaluation of potential bioconcentration was conducted using fathead minnows. + positive control (PFOS), a fluorotelomer alcohol, and a [I Ae Te re AT-L @ > Introduction Acute 96-hr LCsy's PFOS 7.8 mg/L bluegill, 9.5 mg/--L fathead minnow Tel. B Alcohol > WS (140 ppb)-- zebrafish, 316 mg/L-- fathead U-polymer > 1581, 4000 mg/L -- fathead minnow > RSE - Continuous flow-through -- 14 volume renewals/day ~ Negative, positive control (PFOS), 4 test substances - Single test concentration ~ 10 pg/L, as total fluorine - nominal test substance conc's from 13 -- 100 pg/L -1 test chamber/test substance; 70 fish /test chamber -16 L : 8 D photoperiod - 14 d uptake phase, 14 day depuration phase ~ Fish fed ~ 2% body weight; frozen brine shrimp - Loading -- 0.2 g/L/day & @ * CET IE OT - Analysisofstock solutions from Day 0 and Day 13 - Sacrificeoffish, uptake phase: - days 0,2,5,7,9,12, 14 - Sacrifice of fish, depuration phase: -days 16,19,21,23,26, 28 ERNE o-fsasmapmlpelecoamnbducsotnivoenrsuisoinngofWiocrgkabnoilcdFtotrocihn;omrignaenriaclifzluaotriiodne ion selective measurementoffluoride = : & v Wickbold Torch i a oo i op -- : SOlRoo 1 Al a EsL ERIE. ol aL a \ Te SeabeesCase Es f= sti J =i ==, ya] AEat \ bY ` mE [ x RPE a Een mo Bc G , ee te. \l Ca T rBa HB a tr ma FWIea SSH Rioee) L = ony ai ST Stock Solutions - % Recovery of Test Substance as Fluoride Eg Day 0 Day 13 ^ s^ ^ 0'' Test Substance 7.000 6,000 4 5.000 4.000 E 3.000 2.000 0 ^ 1.000 0.000 0 V 0 . PFOS Uptake and Depuration 0 Measured Modeled Uptake A Modeled Depuration 0 ^.A 0 8 5 " 0 0 0 <? 0 ^O^A^AA A m A SS& agt A 0 0,, AA A . V " 5 10 15 20 Day 8.000 -j Urethane Polymer Uptake and Depuration 0 Measured Modeled Uptake A Modeled Depuration 7.000 - 6.000 - 5.000 - JO) 'S 3 fl) 5 4A .0f\0f\0f\ - c 0 ^ "- 3.000 - -- -- -- -- -- -- -- --0 0^ -- -- -- -- 2.000 - ------------------------------------------------------------------S2------Ar-A A A A ^-------------- j 8AAA 0 A v ^ ^/\ 5 0 $ 1.000 - ,, 11B ^ o fl $ 0 0 0.000 B -.- 1! 1'""11 " "-"""1"111 ""1[1 ...........".......,......"....""--...........-.. i -. ........ ....^ ^ , ^ . , , ... C 3 5 10 15 20 Day Zonyl BA (Telomer B Alcohol) Uptake and Depuration 0 Measured Modeled Uptake ^, Modeled Depuration 14.000 ---------------------------------------------------------------------------------------------------------------- 0 0 12.000 10.000 0) ^ 8.000 a>" "o 6.000 4.000 --0 -- - 0----- -- - 0 . v/S 0 AV AA A A,, A A - - - -11 -- ii > 0 ^ <> ' --A 0 0 8 2 o --------^------------B-------------------------------------------------------------------------------------- 0 2.000 ". 0.000 0 5 10 15 20 Day Results No SS for FOS, Polymer or TB Alcohol in 14 days Test Substance 14-d BCE Kk; is BCE-K PFOS PE) 0031 0:04 775 BRITS 5 (TERE AT Tel B Alcohol 1025 0.0883 0.0401 2202 Comparative Results -- PFOS WLI Inc., 2002 Bluegill Sunfish -- 0.087, 0.87 mg/L; 62 d uptake, 56 d dep - 0.87 mg/L terminated @ 35 d3 55/90 fish dead - 0.086 mg/L -- BCF-K; Whole Fish =2796 Martin et al. (2003 a, b) -- ETC 22: 189-195, 196-204 Rainbow Trout - carcass BCF-K = 1100 (~ whole body [Ye ) BSE Fathead Minnow - BCF-K = 775 Comparative Results -- Tel B Alcohol (METI 2002) Carp -- 0.844, 9.22 pg/L; 60 d uptake, 7 d dep. ~ 9.22 g/l -- mean whole fish BCE, max BCF = 1100 A 14d 21d 28d 42d 60d ki) TOR CLRF(1) - Depuration - < LODof26 ng/g within 7 d UTS Fathead Minnow - BCF-K = 2202 AATIELL a OSETR LDV eu _ variability in stock preparation, sample collection, _ variability in sample combustion, fluoride analysis, _ extrapolation from measured F ion in stock solutions to concentrationsiin test solutions, _ assumption that fish residue is entirely parent compound ER TET ECORI ow CE he x Conclusions: ~ screening BCF test approach; reasonable estimates of BCFs based on values from GLP guideline studies, ~e.g., PROS, 775 vs 2796 (fathead minnow, bluegill) ~Telomer B Alcohol, 2202 vs 950 (fathead, carp) the potential bioconcentration of the Telomer B Alcohol is unlikely to be a significant environmental issue based on observed BCE values and its phys-chem properties (low WS, [TER RH TERR - the potential bioconcentrationofthe urethane polymer is also unlikely to be a significant environmental issue based on FINES Do RI