Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Environmental fate & pathways

Endpoint summary

Administrative data

Description of key information

Stability:

Hydrolysis:

On the basis experimental study of the test chemical and applying the weight of evidence approach, the test chemical does not show tendency to hydrolyse. On the basis of this test chemical is cosidered to stable in water.

Biodegradation:

Biodegradation in water:

According to Column 2 of Annex VII the study does not need to be conducted because the test chemical is inorganic.

Biodegradation in water and sediments:

Estimation Programs Interface (EPI Suite, 2018) prediction model was run to predict the half-life in water and sediment for the test chemical. If released in to the environment, 29 % of the chemical will partition into water according to the Mackay fugacity model level III and the half-life period of test chemical in water is estimated to be 15 days (360  hrs). The half-life (15  days estimated by EPI suite) indicates that the chemical isnot persistent in water and the exposure risk to aquatic animals is low whereas the half-life period of test chemical in sediment is estimated to be 135 days (3240 hrs). However, as the percentage release of test chemical into the sediment is less than 1% (i.e, reported as 0.0692 %), indicates that test chemical is not persistent in sediment.

Biodegradation in Soil:

The half-life period of test chemical in soil was estimated using Level III Fugacity Model by EPI Suite version 4.1 estimation database (EPI suite, 2018). If released into the environment, 70.9 % of the chemical will partition into soil according to the Mackay fugacity model level III. The half-life period of test chemical in soil is estimated to be 30 days (720 hrs). Based on this half-life value of test chemical, it is concluded that the chemical is not persistent in the soil environment and the exposure risk to soil dwelling animals is moderate to low.

Bioaccumulation:

Bioaccumulation: aquatic/sediments:

According to column 2 of Annex VIII the study does not need to be conducted because the substance has a low potential for bioaccumulation based on log Low <= 3 (-1.301)

Transport and distribution:

Adsorption/desorption:

According to column 2 of annex VIII the study does not need to be conducted because the substance has a low octanol water parttion coefficient and the adsorption potential of this substance is related to this parameter.

Additional information

Stability:

Hydrolysis:

On the basis experimental study of the test chemical and applying the weight of evidence approach, the test chemical does not show tendency to hydrolyse. On the basis of this test chemical is cosidered to stable in water.

Biodegradation:

Biodegradation in water:

According to Column 2 of Annex VII the study does not need to be conducted because the test chemical is inorganic.

Biodegradation in water and sediments:

Estimation Programs Interface (EPI Suite, 2018) prediction model was run to predict the half-life in water and sediment for the test chemical. If released in to the environment, 29 % of the chemical will partition into water according to the Mackay fugacity model level III and the half-life period of test chemical in water is estimated to be 15 days (360  hrs). The half-life (15  days estimated by EPI suite) indicates that the chemical isnot persistent in water and the exposure risk to aquatic animals is low whereas the half-life period of test chemical in sediment is estimated to be 135 days (3240 hrs). However, as the percentage release of test chemical into the sediment is less than 1% (i.e, reported as 0.0692 %), indicates that test chemical is not persistent in sediment.

Biodegradation in Soil:

The half-life period of test chemical in soil was estimated using Level III Fugacity Model by EPI Suite version 4.1 estimation database (EPI suite, 2018). If released into the environment, 70.9 % of the chemical will partition into soil according to the Mackay fugacity model level III. The half-life period of test chemical in soil is estimated to be 30 days (720 hrs). Based on this half-life value of test chemical, it is concluded that the chemical is not persistent in the soil environment and the exposure risk to soil dwelling animals is moderate to low.

Bioaccumulation:

Bioaccumulation: aquatic/sediments:

According to column 2 of Annex VIII the study does not need to be conducted because the substance has a low potential for bioaccumulation based on log Low <= 3 (-1.301)

Transport and distribution:

Adsorption/desorption:

According to column 2 of annex VIII the study does not need to be conducted because the substance has a low octanol water parttion coefficient and the adsorption potential of this substance is related to this parameter.