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Toxicity to soil macroorganisms except arthropods

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Endpoint:
toxicity to soil macroorganisms except arthropods, other
Type of information:
other: EU Risk Assessment
Adequacy of study:
other information
Reliability:
other: EU Risk Assessment
Rationale for reliability incl. deficiencies:
other: No reliability is given as this is a summary entry for the EU RAR.
Principles of method if other than guideline:
EU Risk Assessment
GLP compliance:
not specified

EU Risk Assessment (2003):


 


The reported EC50 values range between 127 mg/kg (Neuhauser et al., 1986) and 290 mg/kg (Ballhorn et al., 1984).


 


The toxicity to earthworms was studied using the OECD artificial soil test. In the same study, contact tests were performed in which LC50 values of 23 -27µg/cm2 were observed (Neuhauser et al., 1986). In a study on Eisenia foetida over 14 days, an EC50 was observed at 290 mg/kg soil dry weight. The EC0 was 100 mg/kg. The substance was applied dissolved in acetone and nominal concentrations used in the effect estimations (Ballhorn et al., 1984).

Executive summary:

EU Risk Assessment (2003):


 


The reported EC50 values range between 127 mg/kg (Neuhauser et al., 1986) and 290 mg/kg (Ballhorn et al., 1984).


 


The toxicity to earthworms was studied using the OECD artificial soil test. In the same study, contact tests were performed in which LC50 values of 23 -27µg/cm2 were observed (Neuhauser et al., 1986). In a study on Eisenia foetida over 14 days, an EC50 was observed at 290 mg/kg soil dry weight. The EC0 was 100 mg/kg. The substance was applied dissolved in acetone and nominal concentrations used in the effect estimations (Ballhorn et al., 1984).

Endpoint:
toxicity to soil macroorganisms except arthropods, other
Type of information:
other: BUA report
Adequacy of study:
other information
Reliability:
other: BUA report
Rationale for reliability incl. deficiencies:
other: No reliability is given as this is a summary entry for the BUA report.
Principles of method if other than guideline:
BUA report
GLP compliance:
not specified

BUA report (1987):


 


In a study on filter paper 1,2,4-TCB was found to be very toxic toEisenia foetida. The LC50 ranged between 10 - 100 µg/cm² (Neuhauser et al., 1986).


 


In an OECD-Guideline study following results were found: LC0 = 125 mg/kg, LC50 = 250-500 mg/kg and LC100 = 500 mg/kg (Broecker et al., 1984).

Executive summary:

BUA report (1987):


 


In a study on filter paper 1,2,4-TCB was found to be very toxic toEisenia foetida. The LC50 ranged between 10-100 µg/cm² (Neuhauser et al., 1986).


 


In an OECD-Guideline study following results were found: LC0=125 mg/kg, LC50=250-500 mg/kg and LC100=500 mg/kg (Broecker et al., 1984).

Description of key information

For transported isolated intermediates according to REACh, Article 18, this endpoint is not a data requirement. However, data is available for this endpoint and is thus reported under the guidance of "all available data".


 


EU Risk Assessment (2003):
The reported EC50 values range between 127 mg/kg (Neuhauser et al., 1986) and 290 mg/kg (Ballhorn et al., 1984).
The toxicity to earthworms was studied using the OECD artificial soil test. In the same study, contact tests were performed in which LC50 values of 23 -27µg/cm2 were observed (Neuhauser et al., 1986). In a study on Eisenia foetida over 14 days, an EC50 was observed at 290 mg/kg soil dry weight. The EC0 was 100 mg/kg. The substance was applied dissolved in acetone and nominal concentrations used in the effect estimations (Ballhorn et al., 1984).



BUA report (1987):
In a study on filter paper 1,2,4-TCB was found to be very toxic toEisenia foetida. The LC50 ranged between 10-100 µg/cm² (Neuhauser et al., 1986).
In an OECD-Guideline study following results were found: LC0=125 mg/kg, LC50=250-500 mg/kg and LC100=500 mg/kg (Broecker et al., 1984).

Key value for chemical safety assessment

Additional information