Document 1ge88paezKJ2wGQwYVjJ8r0Ra

AR R226 - 07] 2 BIODEGRADATION (OECD 301) TEST SUBSTANCE Identity: ArefmeirxrteudretocaonstPaiFnOiSng, pFeCr-f9i5u,oroorocatsanaescuolmfponoanteen,twohficFhC-m2a03y.al(s1o-be Octanesulfonic acid) (CAS # 2795-39-3). Remarks: The 3M production lot number was not noted. The test sample idSsiuelFttCh-oy2nl0ee3nf.eoagmCleuyrcr,orle3nbt%utiysnlofeodtrihmuearmt,iooc3nt7yi.ln8ds5iucl%faatwteaest,eirt0,.is12a%0m%sioxedttiuhurymeleolnfaeu1rgy.ll3ycs4ou%ll,fPa2tF.eO,6S6a,n%d35% 0.05% tolyltriazole. Tchhaerafcotlleorwiiznegd scounmcmeantrryataipoplnisoefsitmopaurmiitxiteusr.eDwaittha imnacyomnpoltetaeclcyurately reflect toxicity of the fluorochemical componentof the test sample. METHOD TMeestthtoydp:e:MoRdiefaideyd OBiEodCeDgraSdcarbeielntiy.ng Test, OECD 301E, with DOC Analysis GYeLaPr:CoNmopleted: 1983 Analytical monitoring: Dissolved organic carbon (DOC) Statistical methods: Results were determined by calculation of the % DOC removal. Test organism source: A 50:50 mix of soil extract and secondary effluent. The secondaryeffluentwas from the Metro Wastewater Treatment Plant, St. Paul, MN while the soil was from the townof White Bear Lake, Ramsey County, MN. Test coDnidliuttiioonn:water: Not given. Rreeffeerreenncceemaatnerdiatle,stsosodliuutmiobnenpzroeaptaer,atwieorne:prSoelpuatrieodnsonofathe testand _ `weight/volume basis with nutrient solution. TNeusmtbveersoseflsc:oncNeonttgriavteino.ns: 1 plus sodium benzoate standard and blank, all in duplicate. "TToetamlpesruatsupreen:deNdotsogilviedns. and pH on day of testing: Not given. Element Basis: Decrease in dissolved organic carbon compared to the blanks. RESULTS 000464 Nominal concentrations: Blank control, sodium benzoate standard, and test material at ~ 40 mg DOC/L and test material inhibited. Element values: 28-day degradation = 66% mean DOC removal Remarks: Testing was conducted on the mixture as described in the Test Substance Remarks field. The values reported apply to that mixture and not the fluorochemical proportion alone. CONCLUSIONS FC-203 degradation based on the mean DOC removal value was 66% after 28 days. SPauublm,itMtienrn:esot3aM, C5o5m1p3a3ny, Environmental Laboratory, P.O. Box 33331, St. D JALITY Rmeeltiahboilditfyo:llKolwiemdi.scThhreaniknioncgul=u3m. isSntoutdyprloapcekrslydecshcarriapcttieornizaendd. rTechoerdssamopfltehe purity was not properly characterized and the study lacks analytical confirmation of the amount of fluorochemical proportion in the solution. REFERENCES The studies were conducted by the 3M Company, Environmental Laboratory, Lab Request number 9191, 1983. OTHER Last changed: 6/28/00 000465 Fomerrare TECHNICAL REPORT SUMMARY mportontot mpris rinenothefps,snd cpio TGC)Glonoesi. New Method Development 9970030000 Repeat OECD Biodegradation Test on FC-600 and FC-203 R. L. Bohon, Environmental Laboratory/EE & PC, 21-2W-05 6/16/83 E. A. Reiner, Environmental Laboratory/EE & PC, 21-2W-05 47816 EEar None - sccunirvy mr See Environmental Lab Request #9191 DSpenReporiacunmay DiomdReport-Opmsurmmay|SW CHEMIGAL , Cichckbo frhomicscaaeirsihed To test repeatability of modified OECD Screening Tests in measuring the biodegradabiity of "LIGHT WATER" products. A Antwerp "LIGHT WATER" products FC-203 and FC-600. The sparmeeviopursodutcetst lo(tsseeweLraeb used as Request had been #8483). used The in the results of this testing showed poor repeatabiity both between the two sets of tests and between the duplicates in the current reducing variability in the future. [PE Initio: ae" ety ie Ah. we! = perp A \ xh od \o go Eo 000466 OECD Study/EAR Page 2 June 17, 1983 INTRODUCTION The Environmental Lab has conducted two previous modified OECD Screening Tests to determine the biodegradability of "LIGHT WATER" products (1,2). This testing was conducted in accordance with the guidelines current at the time of testing (3,4). The aifferences between the 1979 and 1981 modified OECD Screening Test protocols were of a type that they would not have significantly affected the extent of biodegradation. The first set of testing, that was conducted under LR #5441, showed nearly complete DOC removal (2 928) for all "LIGHT WATER products tested. The results also showed little variability between the duplicates done on each "LIGHT WATER" product (<2%). LR $8483 was undertaken at the request of K. F. Schroeder of 34 Germany in order to confirm the previous biodegradation test results. He made this request because a large amount of variability existed among the biodegradation test results on - "LIGHT WATER" products. This second test showed less complete dedgradation of "LIGHT WATER" products. Due to difficulties with the analytical equiment, from samples from the LR8483 degradation study were analyzed four to 5 months after they were taken). The samples from this study, when eventually analyzed, gave very oo consistent results and results which duplicated those done prior to the onset of difficulties with the DOC analyzer. 000467 Nevertheless, it was decided to repeat the study because of concerns about the reliability of the results after long-term sample storage and because the results showed biodegradation levels less complete than that previously found. This report describes the results of a third set of modified OECD Screening Tests on "LIGHT WATER" products. It is an attempt to repeat the findings of LR #8483 and is done using the same "LIGHT WATER" samples and the same reference compound. METHODS AND MATERTALS The methods and materials used in this screening study were identical to those used in the previous study on FC-600 and FC-203 (2), except that the initial DOC of the "LIGHT WATER" products was initially adjusted to 40 mg/l instead of 20 mg/l. This was done because the first OECD test on "LIGHT WATER" biodegradation (1) showed that 40 mg/l "LIGHT WATER" concentrations were not toxic, and because it was felt that a higher "LIGHT WATER" concentration.a"hAen tpryoveed the sensi. tivity Of the TOC analysis. Inocula for the study which was started on 3/30/83, which - consisted of garden soil from White Bear Lake, MN, and secondary effluent from the St. Paul Metro Wastewater Treatment Plant were collected on 3/30/83. All TOC analyses on samples from the study were done within a week of completion of the study. - RESULTS AND DISCUSSIONS Table 1 summarizes the results of this study. Appendices 1 and 2 000468 contain the actual data sheets and plots of the degradation as a function of time. Degradation of the reference compound, sodium benzoate, was nearly complete within 7 days. FC-203 degradation continued gradually to Day 27 but remained thereafter plateaued at about 65% throughout a l4-day extension of the test. FC-600 reached an average degradation level of 73% during the 28-day test period, and degradation slowly proceeded to the li-day extension of the test to 85% The OECD test procedure stipulates that chemicals should reach 70% DOC removal during the 28-day test period to be considered readily biodegradable. In this set of tests, the average result for FC-600 indicated that it just bearly reached the stipulated level of degradation. The average FC-203 DOC removal did not reach the required 70% level in either the 28-day standard test period or the 42-day extended test period. However, one of the FC-203 duplicates did just exceed this required level of degradation. : The modified OECD Screening Test procedure also stipulates the chemicals considered to be readily biodegradable should complete 708 DOC removal within 10 days of reaching 10% DOC removal. This ~~ stipulation was not met by either of the products. However, this recommendation of the test procedure appears to be intended for pure chemicals and does not make sense when applied to a formulated product such as "LIGHT WATER" since some components may be readily degradable thus allowing a 10% DOC removal quite early in the test period, while other components may be more resistant to degradation, and no degradation may have occurred to 000469 these components during the time that 10% of the DOC total product was removed The controlled data in Table 3 demonstrates the soluble loss from the test samples is not due to physical modes such adsorption, volatilization, or precipitation. These samples were handled identically to the test vessels, except that they contained HgCl to prevent microbial growth. The table shows that at the end of the 28-day test period, these controls contained all of the initial DOC. - Tables 3 and 4 summarize the results of the three OECD screening tests on "LIGHT WATER" products. The first test on "LIGHT WATER products on Lab Request $5543 showed that 3 "LIGHT WATER" products were very degradable. However, these tests were run on samples of European made "LIGHT WATER" products. However, more recent testing on the LR #8483, as well as the data presented in this report, come under LR #9191, showed that "LIGHT WATER" products provided in 1982 were not as degradable. Table 4 shows that the differences between the duplicates in the OECD screening tests also increased with the latter testing. The reasons for this decreased degradation and increased variability are not - known. Contamination of the samples during testing is not the likely cause since great care was taken in washing the glass. Glasses were washed first with soap and then were acid washed with a strong acid dichromate solution and then were triply . rinsed with tap and deionized water. Analytical errors are also not a likely cause of the lower levels of degradation observed or the increased variability between duplicates. This can be stated 000470 because TOC measurements were very precise. Of 50 duplicate T0C measurements made during the test, the main difference was only 0.38 ppm or dissolved organic carbon with the standard deviation of 0.33 ppm. In a 20 ppm test such as that done with the reference compound, this would only account for a 1.9% error plus or minus 3.3% with a 95% confidence level. Ina 40 ppm test such as that done with the two "LIGHT WATER" products, this variability could only have accounted for a 1% error with a 95% confidence interval of +1.7%. Also calculated and measured DOC values for the reference compound were identical Some possible causes for the variability could be the differences between the lots of "LIGHT WATER" products tested. The new lot may contain some toxic components which inhibit degradation or it could contain chemicals components, which are more resistant to degradation than those tested in 1980. A second possibility is that the extract, which was from the same bottle of material used in the 1980 study, may have lost some of its necessary cofactors through age. A third possibility is that the inocula, although taken from the sources, may have had lower levels of viable microorganisms or may have not included organisms with capabilities necessary for rapidly degrading the "LIGHT WATER" - products Possible ways in which these reasons for reduced biodegradation could be tested would be to run parallel tests using not only these samples which we have found to give low levels of degradation but also samples of lots which are known to be within specifications for "LIGHT WATER" products, as well as the FC-203 000471 LIGHT WATER" sample used in the 1980 test, which showed high levels of degradation. Another way to test the results would be to run the screening test, both with the vitamin solution and with the yeast extract. The extract could be used both at the levels called for by the procedure and at higher levels which could provide larger quantities of cofactors during the "LIGHT WATER" degradation process. In addition, this parallel study using an inoculum from an alternate waste treatment and soil source could be run to determine if this has.any effect on degradability. Hopefully, such a series of tests would enable us to ind the causes of low degradability in the higher levels of variability found in the current testing and testing done under LR #8483. CONCLUSIONS Present study did not repeat the findings from previous OECD screening tests on "LIGHT WATER" products which show these products to be "readily biodegradable. In the present study, FC-203 was found to be slightly below the guideline level of 70% DOC removal required for a material to be considered readily biodegradable, while FC-600 showed an average level of DOC . removal just slightly above this required level. Possible reasons for this variability in test results and in ways of Getermining the cause of this variability are discussed. 000472 REFERENCES 1. E. A. Reiner, Biodegradation of "LIGHT WATER" Products in OECD Test 6/80, 34 Technical Report No. 40, Dept. 0535 Project 9970012600, 6/30/80. 2. E. A. Reiner, OECD Biodegradation Testing on FC-600 and FC-203, 3M Technical Report No. 001, Dept. 0535, Project 9972410100, 4/18/83. 3. Modified OECD Screening Test with DOC Analysis, OECD-Chemicals Testing Programme Expert Group C, Degradational Accumulation, Tokyo, December 1, 1979. 4. Ready Biodegradability: Modified OECD Screening Test, 301E, OECD Guideline for Testing of Chemicals Adopted, May 12, 1981. 000473 ane 1 HE BIODECRADATION ee, aw reas (X DOC REMOVAL) OF SODIUM BENZOATE Product SSooddiiuumm BBeennszooasttee #12 Fc0--220033 #112 FFoo--6s0000 1#12 % Degradation at Day: z Ln 2a 2 2 a2 9S3h.s8 9924.s4 %988 =- -z -z 3sea ddeelss ssess e7l0l4 enaa 7se8s w3e8 s4e2o 6s7ss eTeess e1n8s4 1sso Tams 2 PERCENT OF INTIAL DOC IN STERILE CONTROLS AT DAY 28 Product 2 D0C Rematntng Fo-203 100 Fo-600 100 000474 Product FC-203 Fo-206 FC-600 Fe-3017 Sodium Benzoate Bydroquinone TABLE 3 COMPARISON OF PERCENT DOC REMOVAL(a) IN OES CD CRE TESF TSON N"LI IGHTN WATG ER" PRODUCTS IR 5541 937 921 - 95% - 93x IR 8483 797(b) - 862 - 97% - - 18 9191 66% 73% - 972(e) - (2) percent DOC removal was measured at 28 days. (b) peterntned at 27 days. (e) peterntned at 21 days. 000475 TABLE 4 THREE MODIDFIIFEFEDROEENCCFD(S2C)REBEENTIWNEGETNEDSUTPSLOICNAT"ELSIGIRNTWTHAETER" PRODUCTS Product FC-203 FC-206 FC-600 Fe-3017 Sodium Benzoate Hydroquinone LR()s501 0 0.9 1.6 - 3.7 LR 8483 4.6(c) - 12.2 - 5.6 - - LR 9191 11.4 10.9 - 5d) - (8) Difference 1s expressed as of original DOC at 28 days. (b) bLiRod5e54g1rad1astitohne tEeasvti.ronmental Laboratory Request Number of the ) Difference at 27 days. (4 pifference at 21 days. 000476 @ References V Be A Bir, Bodeyrdtin of Lplh pout fu iki on 0ECO Test &/%2, Bm Feckniid Epon No wo, per os3s, Prijet ?9700/2c00 6/3)fo 2) ELA Rie, 0ECO Bideyrdtan 7, Cay om FC=Co0 ant Fe-203, 3m Teknsod Bpirt, hofoo!| ppt oss, payed 997auramo, offs 7 7 3) Mulibid ECO SermisToff GA _0SE nips, OES Clamiicto Tattey Prpumme Gupet Crop, Pegrodibres Accwmiditon, Tokyo, 1, 1975 7) Reedy badgeltly Lfeis ECO Scrinin, Tok 301 & , 0Eco Cudflin fr Tati of Clmik ddloptes Meyitz, ivr, 000477