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Ecotoxicological information

Toxicity to microorganisms

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Description of key information

Reliable toxicity data on micro-organisms are available for strontium and sulfate. Strontium and sulfide are released upon dissolution of SrS in the aqueous environment. Sulfide is rapidly oxidised under natural environmental conditions, and thus, the toxicity of sulfate was considered. However, sulfate is of low toxicity based on the most sensitive endpoint for the presence of stalked ciliates corresponding to a NOEC of ca. 7 g SrS/L.
Regarding toxic effects of dissolved Sr, reliable 3h-IC50 and 3h-NOEC values of >41.4 and >=41.4 mg Sr/L, respectively, was reported by Desmares-Koopman (2010), using Sr(NO3)2 as test substance, corresponding to the 3h-IC50 and 3h-NOEC values of >56.5 and ≥56.5 mg SrS/L.

Key value for chemical safety assessment

EC10 or NOEC for microorganisms:
56.5 mg/L

Additional information

Because of the oxic nature of a typical test systems for this endpoint (activated sludge respiration inhibition tests or single-species tests with ciliates), it is considered technically very difficult to ascertain continuous exposure to a constant strontium sulfide concentration is these specific tests.

Sulfide/sulfate:

Availabe studies with sulfide were considered unreliable because it was not clear if sulfide concentrations were measured, and/or the respective pH was not sufficiently reported. An estimate may be considered based on the lowest available effect concentration, i.e. the 16h-EC50of 1.6 mg S2-/L for the bacteriumPseudomonas putida; Bringmann and Kühn, 1980) corresponding to 5.97 mg SrS/L. However, these data are not relevant for the assessment of SrS.

When active aeration is applied (as is the case during several steps of a sewage treatment plant), any dissolved sulfides are expected to be oxidized to sulfate in less than an hour. Other routes of removal are the precipitation of metals (MeS) as sulfides (e.g. Na2S) are actually sometimes added during the treatment process for this purpose. Because any dissolved sulfide precipitates and is removed from the system or oxidizes to sulfate, read-across to sulfates is justified.

The study of Tokuz and Eckenfelder (1979) was identified as key study of sulfate toxicity to micro-organisms in the OECD SIDS for Na2SO4(the most relevant substance for assessing the risks of sulfate). Therein, activated sludge units were fed with wastewater with Na2SO4concentrations increasing stepwise from 8 to 35 g/L over 37 days. Sludge performance was monitored by measuring BOD, COD and TSS in the effluent, and sludge composition was examined microscopically. The most sensitive endpoint, i.e. the NOEC of approximately 8 g Na2SO4/L for the presence of stalked ciliates corresponds to a SrS concentration of 7 g/L.

Strontium:

A reliable study (Klimisch 1, GLP) of strontium toxicity to microbial respiration inhibition was conducted with activated sludge from a (predominantly) domestic sewage by Desmares-Koopman (2010). An inhibition of the respiration rate was not observed at the highest tested concentration. The 3h-IC50and 3h-NOEC amount to >41.4 and ≥41.4 mg Sr/L, corresponding to a 3h-IC50and 3h-NOEC of >56.5 and ≥56.5 mg SrS/L, respectively.