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Appendix D - Dossier (PDF) - Tera

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date: 20–JUL–2005<br />

3. Environmental Fate and Pathways Substance ID: 71–43–2<br />

______________________________________________________________________________<br />

Type: aerobic<br />

Inoculum: other<br />

Concentration: 1 mg/l related to Test substance<br />

Degradation: > 99 % after 16 day(s)<br />

Method: other<br />

Year: 1985<br />

GLP: no data<br />

Test substance: no data<br />

Method: Removal of benzene in groundwater samples from Gainesville,<br />

Florida (drawn from a 9 m deep shallow).<br />

Batch culture experiments according to Bouwer et al.,<br />

Environ. Sci. Technol. 15, 596–599. Elimination of test<br />

substance monitored by GC–MS. Sterile control.<br />

Result: After an acclimatization phase of 8 days and a period of slow<br />

degradation of 4 days a complete primary degradation of<br />

benzene was achieved between day 12 and day 16. No change in<br />

benzene concentration in sterile control indicates biological<br />

transformation of TS.<br />

Source: Deutsche Shell Chemie GmbH Eschborn<br />

German Rapporteur<br />

Test condition: Incubation at 20 degree C in the dark; pH 5.3<br />

Reliability: (2) valid with restrictions<br />

No standard test procedure, but in accordance with generally<br />

Flag: Risk Assessment<br />

02–SEP–2003 (292)<br />

Type: aerobic<br />

Inoculum: other<br />

Method: other<br />

Year: 1981<br />

GLP: no data<br />

Test substance: no data<br />

Method: The static–culture flask–screening procedure of Bunch R.L. &<br />

Chambers C.W. J. Wat. Pollut. Control Fed. 39, 181 (1967)<br />

modified by Tabak H.H. & Hannah S. Static Procedure for<br />

Biodegradability Determination. Internal EPA Report, Mun.<br />

envir. Res. Lab., Cincinnati, Ohio (1979) was followed.<br />

Wastewater from domestic sewage was used as inoculum.<br />

Benzene was prepared in deionized distilled water as a 10%<br />

solution to give concentrations of 5 and 10 mg benzene/l.<br />

The solutions were incubated with prechilled dilution water<br />

containing 5 mg yeast extract/l, and also with settled<br />

domestic wastewater inoculum. The flasks were then incubated<br />

for 7 days in glass stoppered bottles (to minimize<br />

volatilization) and three weekly subcultures were taken<br />

(totalling 28 days of incubation). Duplicate samples at the<br />

beginning of each incubation period and triplicate samples<br />

at the end of each 7–day period were subjected to GC, total<br />

organic carbon (TOC) and dissolved organic carbon (DOC)<br />

analyses. The minimum sensitivity of the GC procedures used<br />

was about 0.1 mg/l.<br />

Remark: Modification of standard test procedure; method in<br />

accordance with generally accepted standards and described<br />

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

– 207/957 –

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