Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Ecotoxicological information

Toxicity to other aquatic organisms

Currently viewing:

Administrative data

Link to relevant study record(s)

Referenceopen allclose all

Endpoint:
toxicity to other aquatic vertebrates
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):


 


Short-term toxicity to Tetrahymena pyriformis (freshwater aquatic protozoa), Tanytarsus dissmilis (chironomid midge) and Aplexa hypnorum (snail) was studied by Yoshioka et al. (1985) and Holcombe et al. (1987). They found EC50 values ranging from 0,91 mg/l (protozoa) to 3,16 mg/l (snail).

Executive summary:

EU Risk Assessment (2003):


 


Short-term toxicity to Tetrahymena pyriformis (freshwater aquatic protozoa), Tanytarsus dissmilis (chironomid midge) and Aplexa hypnorum (snail) was studied by Yoshioka et al. (1985) and Holcombe et al. (1987). They found EC50 values ranging from 0,91 mg/l (protozoa) to 3,16 mg/l (snail).

Endpoint:
toxicity to other aquatic vertebrates
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 test on Tetrahymena pyriformisan EC50 of 0,91 mg/l was determined after 24 h test duration (Yoshioka et al., 1985).


 


In a flow-through test on Branchiostoma caribaeum after 96 hours a LC0 of 1,5 mg/l and a LC100 of 10 mg/l was found. When 1,2,4-TCB was added to the test system via sediment after 10 days the following toxic endpoints were found: LC0 = 75 mg/kg, LC50 = 200 mg/kg and LC100 = 240 mg/kg (Clark et al., 1987).


 


In a test on teratogenicity 1,2,4-TCB showed an effected on the larval development of Artemia salina (Kerster and Schaeffer, 1983).

Executive summary:

BUA report (1987):


 


In a test on Tetrahymena pyriformisan EC50 of 0,91 mg/l was determined after 24 h test duration (Yoshioka et al., 1985).


In a flow-through test on Branchiostoma caribaeum after 96 hours a LC0 of 1,5 mg/l and a LC100 of 10 mg/l was found. When 1,2,4-TCB was added to the test system via sediment after 10 days the following toxic endpoints were found: LC0 = 75 mg/kg, LC50 = 200 mg/kg and LC100 = 240 mg/kg (Clark et al., 1987).


 


In a test on teratogenicity 1,2,4-TCB showed an effected on the larval development of Artemia salina (Kerster and Schaeffer, 1983).

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".


 


Studies were performed in different test species (Tetrahymena pyriformisan, Branchiostoma caribaeum, Artemia salina, Tanytarsus dissmilis, Aplexa hypnorum), with varying exposure times and revealed following values:


EC50: 0.91 - 3.16 mg/L


LC0: 1.5 mg/L


LC100: 10 mg/L


 


BUA report (1987):
In a test on Tetrahymena pyriformisan EC50 of 0,91 mg/l was determined after 24 h test duration (Yoshioka et al., 1985).
In a flow-through test on Branchiostoma caribaeum after 96 hours a LC0 of 1,5 mg/L and a LC100 of 10 mg/L was found. When 1,2,4-TCB was added to the test system via sediment after 10 days the following toxic endpoints were found: LC0 = 75 mg/kg, LC50 = 200 mg/kg and LC100 = 240 mg/kg (Clark et al., 1987).
In a test on teratogenicity 1,2,4-TCB showed an effected on the larval development of Artemia salina (Kerster and Schaeffer, 1983).



EU Risk Assessment (2003):
Short-term toxicity to Tetrahymena pyriformis (freshwater aquatic protozoa), Tanytarsus dissmilis (chironomid midge) and Aplexa hypnorum (snail) was studied by Yoshioka et al. (1985) and Holcombe et al. (1987). They found EC50 values ranging from 0,91 mg/L (protozoa) to 3,16 mg/L (snail).

Additional information