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ACUTE TOXICITY TO FISH AR226-053Y TEST SUBSTANCE Identity: Paelrsfoluboeroroecfteyrlrseudlftoonaaste,Flduoirdoeaclykylldiammemtohynliaummmodneiriuvmatsiavlte;. m[a1-y Decaminium, N-decyl-N,N-dimethyl-, salt with 11,2.2,33,4,4.5,5,6,6,7,7,8,8,8-heptadecafluoro-1octanesulfonic acid (1:1), CAS # 251099-16-) Remarks: The 14394 referred 3M production lot number was Lot to by the test laboratory as P3025. 1. The test sample The sample was, is L- ilnabwealteedrF(-a1p1p6r1o5x,imLaottel1y. 3T0h-e40te%sttessatmspulbestisanacem,ix6t0ur-e7o0f%twhaeteters,tasnudbs0t-a5n%ce of residual perfluorochemicals). The test sample appears to be a All values reported relate to this 2-phase dispersion (clear liquid mixture. with opaque solid) were made to which adjust rapidly for the separates after agitation. No calculations actual concentration of the test substance in the test sample. METHOD Method: OECD 203 Type: Static acute GLP: No Year completed: 1996 Species: Pimephales promelas Supplier: Not noted. Analytical monitoring: monitored daily. DO, pH, temperature, and conductivity were Exposure period: 96-hours SStpaetairstmiacna-lKmaertbheordmse:thLoLds.o vTahleueNsOcEalLcuwlaatsedcaulsciunlgattehdeuTsriinmgmFeidsher's Exact tests. Testfish age: Not given. Length and weight: Average length = 11.3 mm, Average weight = 7.8 mLogading: 0.26 glL Pretreatment: None Test conditions: Dilution water: DweacshlaoerriantaetdedfoCri2t4y-ohfoDuurlsutphr,iorMtNo tap use water. in the Water test. C042C2 Dilution water chemistry: hardness: 48 mg/L as CaCO, pH: 8.08 Lighting: lCigohotl,-8w-hhiotuerfslduaorrekscuesnetd.bulNbos.trPanhsoittoiponerpieordioodfn1o6t-ehdo.urs fSrtaoctcikonasn. dTetsetstsosloultuitoinosnwperreepaprraetpiaorne:d Water accommodated individually for each test sreupblsitcaatnececoinnc4enLtroaftidoilnutbiyonmwaastser.addTihtieonsoolfutviiognosrowuesrley svihgaokreonustleyst spthiarrseed wfoars21s-ihpohuornsed(vforrtoemxt1h/e2vteoss1e/l3 astolmuitdi-odnepdtehp.th). The aqueous CStoanbcielinttyroaftitohnestedsotscinhgemriactea:lOsnocluetions: Not noted. EThxepojsarusrweevreessseelasl:ed 4w-iLthglTaesfslojna-rlsinceodntlaiidsnifnitgte3d-Lwiotfh tsetsotpspoelurtsiotno. accommodate oxygen flushing of headspace. Number of replicates: two NNuummbbeerroofffciosnhcepnetrrarteipolnicsa:tet:htreene plus a negative control Water chemistry during the study: Dissolved oxygen range (0 -- 96 hours): 9.1 14.6 87-182 mglL mg/L (control exposure) (700 mg/L exposure) pH range (0 -- 96 hours) 7.80 -8.08 (control exposure) Test 7.78799 temperature (700 mg range (0 -- exposure) 95 hours) 20.8-20.9C Conductivity range (0 - 96 hours): 128 -- 142 umhos/cm (control exposure) 118 - 154 mhos/cm (700 mg/L exposure) bReefmoarreksse:aliOnxg yignietinalwlyaasnaddadteedactoh tohbesehrevaadtsiponacpeeriinodt.heTjhares tdeisstsovlevsesedlos,xypgaertniccuolnacrleyntinratthieon7s00wemrge/sLuepxeprossautruerated in the concentration. RESULTS Nominal Element loading concentrations: value: 24-hour LLso = 618 Bk control, 400, 700, (568 - 673) mg/L. 1,000 mg/L. 48-hour LLso = 607 (554 - 664) mg/L C042C3 72-hour LLsp = 595 (551 - 643) mg/L 9886--hhoouurr LNLOsEo L= 5=6<24(9502m3g-/6L04) mg/L All element values based on nominal concentrations. Biological observations after 96-hours: No mortality or abnormal behavior observed in the negative control during the test. Mortality was oohobbussreesrr,vveeaddndiinn2thfahilesfhorfewmetarhieenifqniusgiheeasxtcpetonhsteua7rt0e90c6o-mnhgco/euLnrtser.xaptNiooosnusar.benSocuorrnmfcaaelcnitbnregahtawivaoinsoartw2a4sobserved in the 400 mg/L exposure concentration. Cumulative percent mortality: LCoosinnng oTons| 20n0us | spurs | 7200s hoomal |&| 5|,| [oo[0[6[6| | FmTw[oe[wo [w] Coo[0| wo| 00 | ww | Lowest concentration causing 100% mortality: 1,000 mg/L Mortality of controls: None Remarks: Values reported are for the test sample. No calculations were made to adjust for the concentration of the test substance in the test sample. cCoONNoCwLuUsSiIOoNnSs The test sample 96-hour LLsofor fathead minnow was determined to be 5no62obmsge/rLvweidthefafe9ct5s%lecvoenlf(iNdOenEcLe)iwntaesrv<al49of0 5m2g3/L-.604 mg/L. The 96-hour `Submitter: 31 Company, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133 ba0 DAtTaAQQuU0 AALbIyTYy 000000 Reliability: Kiimisch ranking 2. The study lacks analytical measurement of test substance concentrations in the test solutions and sample purity is 04234 tnooxticsiutfyficcainenntolty bchearpoascitteirviezleyd.attArdidbiuttieodnatloldy,iddeactyalidsifmoertahymlixatmumroeniaunmd sPoelruftliuoonrsoowcittyhlsouxlyfgoneantecosualltd aallosnoe.haAvleso,consturpiebrustaetdurtoattihoen toofxitcihtey.test R0 EREFFEERRE0 ENNCESS00000000 DTihviissisotnu,dyDuwluatsh,coMnNd,ucattetdheatreAqSucelstCoorfptohreat3ioMn,CoEmnpvairnoyn.mental Testing OO OTTHER OOO Last changed: 5/24/00 C04R35 EAn5i4r1oCrompeonSrsatiisToonn0ii0AnSgSeBDoruetnan STUDYTITLE ACUTE TOXICITY OF `33% DEVELOPMENTAL MATERIAL TO FATHEAD MINNOW (PIMEPHALES PROMELAS) DATA STANDARD OECD GUIDELINE 203 STUDY COMPLETED January 2, 1997 TESTINGFACILITY AScl Corporation/AScl-Duluth Environmental Testing Division 4444 Airpark Boulevard Duluth, MN 55811 Tel. No. (218) 722-4040 Fax No. (218) 722-2592 STUDYIDENTIFICATIONNUMBERS AScI Study ID# 5010-068 3M Company Lab Request# P3025 SSpoonmsaorn, Sl3yM'C1o0mpPanyS 1 04236 EancvliAoCnSomrepSnoaruadiToon1s/8AiS0cD1-0Di.uo5t0un8h 1.0 GENERAL INFORMATION Study Title i 1| | `Sponsor's Representative Sponsor's Lab Request? li Testing Facility I Principal Investigator Acute Toxicity of P3w< Developmental pMraotmeerliaasl).to Fathead Minnow (Pimephales OECD Guideline 203 S3eMrviEcnevsi,roBunimlednitnagl 2T-e3cEh-n0o9l,o9g3y5anBdusShafAevteynue, St. Paul, MN 55133. | Susan A. Beach, 3M Environmental `Technology and Safety Services, Building 2- I [ps 3E-09, 935 Bush Avenue, St. Paul, MN 55133, Tel No. (612) 778-7452. TAeSsctlinCgorDipvoirsaitoino,n/4A4S4c4I-ADiurlpuatrhk EBnovuilreovnamred,ntal [oeDierkes| Duluth, MN 55811; Tel. No. (218) 722-4040. Testing Facility Director Definitive Test Dates Data Validation and Report Review Donald Mount. December 17-21, 1996. Alan Mozol, Be Retention of Raw Data and Final Report I Location of Raw Data and Final Report 1 _ Two years from the date study is compl4eted. |i `ASel Corporation/ASel-Duluth Environmental Testing Division, 4444 Airpark Boulevard, Duluth, MN 55811; Tel. No. (218) 722-4040. SSppoonnsioorr: Su3byCIoDmspPaangyes 2 04237 + EAuSneilroCnmoemnpiosrlaiToensttaiSneglD-Diuvliustohn `ASel Su 104 5010-068 2.0 OBJECTIVES) Tteostdseutbesrtmainncee,th#e 7965-h LDLe,vel(loeptmhaelntlaoladiMantge)raianld, 9f6o-rh fNatOheEaLd m(nionnoobswer(vPeidmeepfhfaelcteslopardoimnegl)aso).f the `GTuhiidsesltiundey2w0a3s(cOoEndCuDcte1d993a)c.corTdhiengtetsot the AScl solutions study were wplaatnerr-eatacicnoemdmboydattheedSfproancstoiornsan(dWOAFE)CD || prepared following Girling, Whale, & Adema 1994. | 3.0 TEST METHODS [| rest substance I || | Test Organisms I Pordooprelretsisess:lurr3yca>ft5er a,gittwaot-iponh,assepelciiqfuiicd before gravity acgai.ta1t.e2d,g/lcicg,htacnodloirnesdo,lunbelaerly | in water. Tmegs/tL.loaTdeinsgts:loa0di(ndgilsuotliuotniownastewrerceontprroelp)a,re4d90inmdgiv/iLd,ua7ll0y0 fmogr /eLacahndtes1t 000 replicate. vigorously The 490 mg/L solutions shaken test substance in were prepared 4 L of dilution by placing 1960 mg of water. The 700 mg/L and and 1000 4000 mg/L solutions were mg of test substance, prepared in the same manner using 2800 mg respectively. The solutions were vigorously stirred (vortex siphoned from 1/3 the to 1/2 vessel astolmuitidondedpetphth) for 21 h. The aqueous phase was | | Source: Healthy, juvenile fathead minnows (Pimephales promelas) obtained from a commercial supplier. Holding/acclimation: Held and acclimated for 12 days in the test dilution water. entire For the 12 days, 48 hours mortality preceding was 0%. the At test test 0% mortality occurred. For termination, the fish were 1.1 the cm in mean length and 7.8 mg in mean weight Use in test: Used 10 organisms/replicate and 2 replicates/test concentration. SSppoonnssoorr: Su3dMy CIoHmpPa3n0y25 3 04228 [I pitution Water Exposure | chambers |l | | Observations | Endpoint Calculations EAnSveilcAoCnSmSoenriSaptl yoTre1n0a3gt0iD1Di0ovu.itns0ia6so8n Scohuermciec:al Daencalhylsoirsiniasteind RCaitwy DoaftDaulPuatchk,agMe.N, tap water. The most recent CChaarCaOct)eraisntdicas:pHAoft8e.st08t.imeA,erthaetewdatfeorr 2ha4dhaphraiorrdnteossusoifng48inmtgh/eLfes(ta.s aTcypceo:mm4o-dLatgelaossxyjgaresnsfelaulsehdinwgiotfhhTeeafdlsopna-lcien.ed lids fied with stoppers to tUesste, ikneptetstc:ove3reLd,ofedxicleupttiownhweanteerxpoerritmesetntsaolluotbisoenr/vcahtaimobnesr.werDeurmiangdethoer | headspace exposures. was flushed with oxygen. Solutions were not aerated during the Duration: 96 h. Daily photoperiod: fluorescent bulbs. 16 h light and 8 h dark, maintained using cool-white Temperature: 21C. Bsitroelsosg,icaanld: Dailydead test Toersgtanoirsgmas.nisms with abnormal behavior and signs of dWaaitley-r tcehmepmeirsattruy:re,(1D)OA,tctoensdtuicntiitviiattyi,onantodtaplH.hardAnlelsdseatenrdmianlkaatliionnisty,we(r2e) `made according to APHA methods (1995) 2o4b-s,er4v8a-b,le72e-f,feactndlo9a6d-ihngme(dNiOaEnL)lethal loading (Lys), and 96h no LLgy Trimmed Spearman-Karber method. WNyOoEmLi:ngT.OXSTAT statistical software, Version 3.2, University of SSppoonnssoorr: Su3dMyCDoAmpPa2n0y25 4 04239 EAnvtrAoCmSomapSroaaryTions1Ai0n8SgeSoD1D0ou00nt8 3.0 RESULTS Test Substance Toxicity (Pertinent data are in | 24-h LLyy: 618 mg/L (368-673 mary, ] | Table 1) 48h LLgy: 607 mg/L (554-664 mg/L). | | 72h LLgy: 595 mg/L (551-643 mg/L). | 96h LL 562 mg/L (523-604 mg/L). { Ranges of Water Chemistry Parameters | 96-h NOEL: <490 mg/L. Total hardness (as CaCO, mg/L): 44-43. Alkaliniy (as CaCO, mg/L): 44. I Temperature (C): 20.8-20.9C. { | DO (mg/L): 8.6200. PH: 7.71-8.08. - Specific conductivity (umhos/em): 118-487. | 4.0 TEST QA/QC | Morality in control exposure must not be more| 0% dead. than 10%. The lowest DO concentration at test staetrumriantaitoinonvamluusetatbeteastt tleeamspter6a0tu%reo.f the air { | SSphoonmsoerr. S3tMyC0o4mpaFancyes The lowest DO concentration measured was 9Af7t%eroifnittihael a0i-rhsoautrurraotuitoinnevaclhueemiasttr2i1e.s0hCa.d ebaecehn cphearmfboerrm'esd hteheadcshpaamcbeewrassweflrueshseedalweidthand oxygen daily Ensuing DO to maintain adequate DO, concentrations were 100% of saturation or greater. s G04R40C Test duration must be 96 h. oRpetfioenraeln)c.e substance toxicity test (this test is EAriSrNoCmSommepSnoaryiToon1/s0A4iSSeD1Dium0to8an "The test duration was 96 h. Control toxicity chart for testing is sodium in Raw cDhaltoariPdaeckraegfee.rence 5.0 REFERENCES | American Public Health Association (APHA). 1995. Standard Methods for the Examination of | Water and Wastewater. APHA, Washington, D.C. | Girting, AE. G.F. Whale, and D.M.M. Adema. 1994. A Guideline Supplement for Determining the Aquatic Toxicity of Poorly Water-Soluble Complex Mixtures using WaterAccommodated Fractions. Chemosphere, Vol. 29, No. 12, pp. 2645-2649. Hamilton, M.A., R.C. Russo, and R.V. Thurston. 1977. Trimmed Spearman-Karber Method for Estimating Median Lethal Concentrations in `Toxicity Bioassays. Environ. Sci. Technol. | 11(7):714-719; Correction 12(4):417 (1978). 1 Organization for Economic Cooperation and Development (OECD). 1993. OECD Guidelines for Testing of Chemicals. OECD Publication Information Center, Washington, D.C. {Universityof Wyoming. 1996. Toxstat Version 3.2. Laramie, Wyoming. SSppoonsoorr: uItMy CIofmpaP3n0y25 . 04241 E5n1rCoopanoyrTnosiotnabioauaost TABLE 1. ACUTE TOXICITY OF 73+" MINNOWS (P. promelas) DEVELOPMENTAL MATERIAL TO FATHEAD or [TestLosvuibsnugnee = =[a Cumulative Number of Dead Organisms and Percent Moralin | a=t Tse e t |ose esTToww e T|a wo) o] [EES-- ee NOT beeen] eam EFFECT AND NO-EFFECT LOADINGS WITH CORRESPONDING 95% CONFIDENCEINTERVALS me Tw] Coen To 2 SSyomonna, St38y8 C5o8mpPaneys , 04242