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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Hazard for aquatic organisms

Freshwater

Hazard assessment conclusion:
PNEC aqua (freshwater)
PNEC value:
0.1 mg/L
Assessment factor:
1 000
PNEC freshwater (intermittent releases):
1 mg/L

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.01 mg/L
Assessment factor:
10 000

STP

Hazard assessment conclusion:
no emission to STP expected

Sediment (freshwater)

Hazard assessment conclusion:
PNEC sediment (freshwater)
PNEC value:
0.082 mg/kg sediment dw
Extrapolation method:
equilibrium partitioning method

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
0.008 mg/kg sediment dw
Extrapolation method:
equilibrium partitioning method

Hazard for air

Air

Hazard assessment conclusion:
no hazard identified

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
PNEC soil
PNEC value:
0.019 mg/kg soil dw
Extrapolation method:
equilibrium partitioning method

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no potential for bioaccumulation

Additional information

Conclusion on classification

The following reliable data is available for environmental classification of this titanate:

Acute Aquatic Toxicity:

Short-term toxicity to fish:

The 96-h LC50 (mortality) to Leuciscus idus, 275 mg/L based on nominal concentrations (read-across from ethyl acetoacetate; European Chemicals Bureau 2002)

Short term toxicity to invertebrates:

The 48-hour EC50 (immobilisation) to Daphnia magna, > 35 ethyl acetoacetate per litre and > 9.8 mg isopropyl alcohol per litre based on the measured TWA concentrations of the hydrolysis products (OECD 202; Tobor-Kaplon M.A. 2013).

The 48-hour EC50 (immobilisation) to Daphnia magna, > 100 mg/lbased on estimated test item concentrations (OECD 202; Tobor-Kaplon M.A. 2013).

Toxicity to algae:

The 72h-EC50 (growth rate) to Pseudokirchnerella subcapitata, > 42 mg ethyl acetoacetate per litre and > 11 mg isopropyl alcohol per litre; based on the measured TWA concentrations of the hydrolysis products (OECD 201; Tobor-Kaplon M.A. 2013).

The 72h-EC50 (growth rate) to Pseudokirchnerella subcapitata, > 100 mg/lbased on estimated test item concentrations (OECD 201; Tobor-Kaplon M.A. 2013).

The 72h-NOEC (growth rate) toPseudokirchnerella subcapitata, 42 mg ethyl acetoacetate per litre and 11 mg isopropyl alcohol per litre, based on the measured TWA concentrations of the hydrolysis product (OECD 201; Tobor-Kaplon M.A. 2013).

The 72h-NOEC (growth rate) toPseudokirchnerella subcapitata, 100 mg/lbased on estimated test item concentrations (OECD 201; Tobor-Kaplon M.A. 2013).

Conclusion: No acute aquatic toxicity as the lowest of the available toxicity value is > 100 mg/l.  

Degradation:  

Abiotic degradation (hydrolysis): Hydrolytically unstable, Half-life less than 10 minutes @ 25 deg. C (OECD 111)

Main organic decomposition products are non-toxic to aquatic environment and readily biodegradable (isopropyl alcohol; > 70 % at 20-d biodegradation, Price et al. 1974) and the biodegradation of ethyl acetoacetate after 28-d is 66 %. After 7 days, 65 % ethyl acetoacetate was degraded and 10-day window was fulfilled (European Chemicals Bureau 2002).

The aquatic toxicity values (EC50/LC50) of the isopropyl alcohol (IPA) based on the literature are:

Scenedesmus quadricauda, 1800 mg/l in freshwater

Daphnia magna, 6850 mg/l in freshwater

Daphnia magna, >10 000 mg/l in freshwater

Artemia salina, >10000 mg/l in artificial sea water

Pimephales promelas, 9640 mg/L in fresh water

Pimephales promelas,11130 mg/L in lake superior water

Rasbora heteromorpha, 4200 mg/L in fresh water

For ethyl acetoacetate the aquatic toxicity values in the literature are the following:

The 48-h LC50 (mortality) to Leuciscus idus; 275 -575 mg/l (European Chemicals Bureau 2002)

The 24-h EC50 (immobilisation) to Daphnia magna; 790 to 800 mg/l based on nominal test concentrations. LC100 values varied between 1250 to 1136 mg/l, respectively (European Chemicals Bureau 2002).

The 72-h EC50 (growth rate) to Desmodesmus subspicatus; > 500 mg/l based on nominal test concentrations (European Chemicals Bureau 2002).

Conclusion: rapidly degradable.  

Bioaccumulation:

Log Kow for the main degradation products (isopropyl alcohol; 0.05 and ethyl acetoacetate; 0.25). Not possible to determine for the target substance because of rapid hydrolysis.  

Conclusion: No chronic aquatic toxicity as the lowest available toxicity value (72 -h NOEC for algae) for the substance itself is 100 mg/l, substance is rapidly degradable, and the degradation products have low potential for bioconcentration and bioaccumulation.  

Environmental classification:

In accordance with EC Regulation 1272/2008 (CLP):

Not classified as hazardous

In accordance with DSD (Directive 67/548/EEC):

Not classified as hazardous