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Ecotoxicological information

Short-term toxicity to aquatic invertebrates

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Administrative data

Link to relevant study record(s)

Description of key information

Testing is not scientifically justified as this substance is hydrolytically unstable.Thus, toxicity of the decomposition products is used as a key value in CSA.

Key value for chemical safety assessment

Fresh water invertebrates

Fresh water invertebrates
Effect concentration:
1 300 mg/L

Additional information

When this substance comes in contact with water or moisture, a complete hydrolysis will take place with no significant reaction products other than n-butanol and hydrated titanium dioxide (half-life < 2 hours, Brekelmans 2013). The organic decomposition product n-butanol is readily biodegradable and not persistent based on the log Kow value of 0.84. The CSA indicates that toxicity of this substance is similar to the main degradation product n-butanol.

Key studies (short-term toxicity to daphnia and algae) conducted for the analogue category member (titanium tetraisopropanolate CAS 546-68-9) justify that these organometallic titanates hydrolyse during toxicity testing and the aquatic toxicity is similar to the alcohol released in water. Category and read-across justifications are presented in the annexes of the CSR. Therefore, a short-term toxicity study on invertebrates is unjustified, and the key value for CSA is obtained from the studies conducted for n-butanol.

Two categories of highly water reactive titanates and moderately water reactive titanates are formed from the eight analogue organometallic titanates, because they all are hydrolytically unstable, and have mechanistic reasoning for read-across from the degradation products within the categories. The source substance for this target substance is n-butanol. The analogue organometallic titanate (bis(ethyl acetoacetato-O1', O3') bis(2 -methylpropan-1 -olato)titanium from the category of moderately water reactive titanates contains and releases 2-methylpropan-1-ol, which is an analogue to n-butanol released from this target substance. The structural analogy of 2-methylpropan-1-ol (CAS no 78 -83 -1) and n-butanol (CAS no 71-36-3) has also used to support the environmental hazard assessments of these alcohols in OECD SIDS initial assessment reports published by UNEP ( UNEP publications 2001 & 2004). Therefore, the toxicity of 2 -methylpropan-1 -ol is used in this weight of evidence approach to evaluate the toxicity of the target substance together with n-butanol data.

Based on the published study results, the 48-h EC50 (immobilisation) of n-butanol to Daphnia magna is 1983 mg/l (with 95 % CL of 1897 - 2072 mg/l) and the 24-h EC50-value 2237 mg/l (95 % CL 2117 -2363 mg/l), respectively ( Kuehn et al. 1989). According to Bringmann, G. & Kuehn, R. (1977), the 24-h EC50 (immobilisation) to D.magna is 1855 mg/l. Similar results have also been reported for 2 -methylpropan-1-ol (the 48 -h EC50, 1300 mg/l with CL 95 % 1200 -1400 mg/l; Elnabarawy et al. 1986).

In conclusion, as a conservative approach the lowest toxicity value of the degradation products is used as key value for CSA.