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Appendix D - Dossier (PDF) - Tera

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date: 20–JUL–2005<br />

4. Ecotoxicity Substance ID: 71–43–2<br />

______________________________________________________________________________<br />

4.4 Toxicity to Microorganisms e.g. Bacteria<br />

Type: other: Microbial toxicity in soil medium<br />

Species: other bacteria: Polytox commercial microbial test culture<br />

Exposure period: 10 hour(s)<br />

Year: 1998<br />

GLP: no<br />

Remark: A laboratory procedure using automated respirometry was<br />

developed to measure microbial toxicity in soils as a<br />

function of respiration inhibition. Sterilized sandy loam<br />

soil; source: agric field, N.M USA, organic content 0.7%,<br />

autoclaved 7hr/4d, 200g/test system; remoisturized w/ dH2O<br />

to 33, 50, 80 and 100% moisture to determine % moisture<br />

effects on toxicity. Microbes: Polytox, commercial<br />

freeze–dried product – blend of 12 strains of aerobic<br />

microbes– supp Polybac Corp. Bethlehem, PA. EPA recommended<br />

microbial culture for effluent tox testing(doc 440/4–87–005,<br />

7/1987).Cells resuspended in nutrient buffer, and 1:10<br />

dilution of resuspended cell volume to soil mass used for<br />

testing. Cell density of inoculum not reported. Acetone<br />

was used as a cosolvent for chemical addition.<br />

Concentration verification of spiked soils by GC/MS<br />

indicated homogenous soil concentrations. During a 10 hr<br />

test duration, respiration was monitored. IC50 calculated<br />

based on reduction of oxygen uptake rate in chemical test<br />

systems versus control reator. The test protocol was<br />

reproducible with a mean standard deviation of 0.08 mg<br />

chemical/g of soil for eight chemicals.<br />

Effect of acetone (as cosolvent) is unclear, since solvent<br />

blank (0.5 ml acetone/200 g soil) preparation is described<br />

as a control system. Determination of IC50 is calculated by<br />

comparison of respiration rates of chemicals to control; it<br />

is not clear if the control contains only soil, or acetone<br />

in soil. IC50 values for acetone are also reported, which<br />

infers soil blanks where used as comparison. It is also<br />

unclear whether the acetone concentration used as co–solvent<br />

affected respiration. Toxicity is not significantly<br />

affected by % mositure for these chemicals.<br />

Result: Benzene IC50 Values at Different Soil Moisture–Holding<br />

Capacities (mg chemical/g soil)<br />

Moisture –holding capacity<br />

33% 50% 80% 100%<br />

IC50 0.51 0.51 0.48 0.30 0.75 0.71<br />

n1 4 6 6 7 4 4<br />

r2 0.990 0.916 0.985 0.690 0.844 0.965<br />

Correlation between toxicity tests done in aqueous medium<br />

and soil for Polytox test culture was statistically<br />

significant and yielded an r2 of 0.816.<br />

In comparison, benzene was determined to have an IC50 value<br />

of<br />

679 mg/l for the Polytox culture in aqueous medium.<br />

Source: Exxon Biomedical Scineces, East Millstone, NJ, USA<br />

<strong>Appendix</strong> D: Benzene SIDS <strong>Dossier</strong><br />

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