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ANA,I Cc LLZORATOas <br /> Sparoer Hazardous Waste/ sample AC27217, AC27218 Nove 1993 Face ♦ 2 <br /> INTRODUCTION <br /> An acute toxicity test was performed on samples AC27217 and AC27218. The samples were <br /> submitted for testing on November 2, 1993. Testing was initiated on November 4, 1993. The test <br /> was a 96 hour static acute bioassay for hazardous waste samples using the minnow, Pimepheles <br /> promelas. <br /> The test was performed following procedures outlined in Polisini and Miller (190o). The static <br /> nonrenewal test was conducted for a 96 hour exposure period. Each sample was tested using <br /> three concentrations to determine whether it should be classified as a hazardous%:aste according <br /> to the criteria established in the California Code of Regulations Title 26, Section 22-60261.24(6). <br /> These criteria state that wastes are to be classified as hazardous if an aquatic toxicity test <br /> conducted with fathead minnows (Pimephales promelas) results in LC50 values less than 500 <br /> ppm (ma/1). <br /> METHODS <br /> Test organisms were obtained from Aquatic Resources, and were held at 20° C for more than ten <br /> days before testing. Fish were 45 days old at the start of the tests on November 4, 1993. <br /> Test conditions are summarized in Table 1. The test was conducted in a temperature controlled <br /> room at 20 -* 2`C, with a photoperiod of 16:8 L:D. Each test treatment used two replicates with <br /> ten organisms per replicate. Test chambers were 5 gallon tanks with 10 liters of t_st solution per <br /> replicate. <br /> Concentrations tested were 750 mg/l, 500 mg/l, and 250 mg!l, as recommended for screening <br /> assays. Aliquots of the sample were weighed into screw-top Erlenmeyer flasks, 200 ml of dilution <br /> water were added to each flask, and the flasks were shaken on a wrist action shaker for six <br /> hours. Dilution water was EPA soft water prepared with reagent grade chemicals and Super-0 <br /> water foilowing EPA protocol (1.990). The samples were added to the test tanks and the test was <br /> initiated by randomly adding ten minnows to each tank. Survival and water quality parameters <br /> were measured and recorded daily. <br /> QUALITY CONTROL <br /> As part of an ongoing quality control program, a reference toxicant test was conducted within the <br /> week prior to the hazardous waste tests. Reference toxicant test results are summarized in Table <br /> 1. Reference toxicant test data sheets and statistical analyses are included in Appendix 13. The <br /> Pimephales promelas reference toxicant test used EPA Mod Hard as the diluent control, and test <br /> concentrations of 3.1, 6.25, 12.5, 25, and 50 mgll sodium dodecyl sulfate. The test was <br /> conducted for a 96 hour exposure period, under the same test conditions as the hazardous <br /> waste tests. Review of test results showed that the control treatment had 100% surviva[ at 96 <br /> hours, meeting test acceptability criteria of at least 90% survival. The LC50 was computed by <br /> the Probit Method to be 23.2 mg/l, within one standard deviation of the lab mean of 24.16 mall, <br /> based on 23 tests. <br /> Tn,s feaors-s ac:;:,caL e.n>y tc:"e samc,e'ece vea 5,srF.aacrarory The Irawtity of the IabaratP y s :ee tc tre amount caro for r^ Trc,s ra <br /> e,c'uslve use-.trc c•r,t is. ihom o is atle•essec a^C,,00r.:-.e congwon that the chem assumes an I,ar -tv for:^e'unr,er a stnesoc :-e e- c• '_ tor'A u <br />