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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Hazard for aquatic organisms

Freshwater

Hazard assessment conclusion:
PNEC aqua (freshwater)
PNEC value:
0.088 mg/L
Assessment factor:
10
Extrapolation method:
assessment factor
PNEC freshwater (intermittent releases):
0.055 mg/L

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.009 mg/L
Assessment factor:
100
Extrapolation method:
assessment factor

STP

Hazard assessment conclusion:
PNEC STP
PNEC value:
1.35 mg/L
Assessment factor:
100
Extrapolation method:
assessment factor

Sediment (freshwater)

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

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
0.31 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:
0.57 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

According to Article 13 of Regulation (EC) No. 1907/2006 "General Requirements for Generation of Information on Intrinsic Properties of substances", information on intrinsic properties of substances may be generated by means other than tests e.g. from information from structurally related substances (grouping or read-across), provided that conditions set out in Annex XI are met.

Annex XI, "General rules for adaptation of this standard testing regime set out in Annexes VII to X” states that “substances whose physicochemical, toxicological and ecotoxicological properties are likely to be similar or follow a regular pattern as a result of structural similarity may be considered as a group, or ‘category’ of substances. This avoids the need to test every substance for every endpoint”.

Since the group concept is applied to the members of the alkyl sulfates category, data will be generated from a representative category member to avoid unnecessary animal testing. Additionally, once the group concept is applied, substances will be classified and labeled on this basis.

 

Classification related key information of CAS 94200-74-5:

Biodegradation in water: readily biodegradable (OECD 301 B)

Bioaccumulation: no potential to bioaccumulate, log Pow = 2 at 20 ºC (OECD 123)

Water solubility: > 400 g/L at 20 ºC (OECD 105)

 

Acute toxicity:

- For fish: 96h LC50 (Pimephales promelas) = 29 mg/L (measured concentration, freshwater, OECD 203, read-across from CAS 151-21-3), 96h LC50 (Cyprinodon variegates) = 4.1 mg/L (measured concentration, marine water, ASTM E-35 1980, read-across from CAS 151-21-3)

- For invertebrates: 48h EC50 (Ceriodaphnia dubia; immobilization) = 5.55 mg/L (nominal, freshwater, read-across from CAS 151-21-3), 48h LC50 (Artemia salina) = 3.15 mg/L (nominal concentration, marine water, read-across from CAS 151-21-3)

- For algae: 96h EC50 ( Pseudokirchnerella subcapitata; growth rate) = 117 mg/L (nominal concentration, read-across from CAS 151-21-3)

 

Chronic toxicity:

- For fish: 42d NOEC (Pimephales promelas; mortality and growth) ≥ 1.357 mg/L (measured concentration, read-across from CAS 151-21-3)

- For invertebrates: 7d NOEC (Ceriodaphnia dubia; reproduction) = 0.88 mg/L (measured concentration, EPA-600/489/001, read-across from CAS 151-21-3)

- For algae: 96h EC10 (Pseudokirchnerella subcapitata; growth rate) = 12 mg/L (nominal concentration, read-across from CAS 151-21-3)

 

Classification justification according to CLP:

Based on the data above, C12-isoAS Na (CAS 94200-74-5) is considered to be rapidly degradable and has a low potential for bioaccumulation. The acute aquatic toxicity L(E)C50 are above 1 mg/L for fish, invertebrates and algae. Valid chronic toxicity data are available to fish, invertebrates and algae – the lowest NOEC is 0.88 mg/L (thus in the range of > 0.1 to < 1 mg/L) for aquatic invertebrates. C12-isoAS Na (CAS 94200-74-5) needs to be classified and labeled as environmental hazard Chronic Cat. 3 according to the Regulation (EC) No.1272/2008 (CLP) and the Regulation (EU) No. 286/2011 (2nd ATP).

M-factor for acute aquatic toxicity:  not need to be assigned

M-factor for chronic aquatic toxicity: not need to be assigned 

 

Classification justification according to DSD:

Based on the data above, C12-isoAS Na (CAS 94200-74-5) is considered to be rapidly degradable and has a low potential for bioaccumulation. The acute aquatic toxicity L(E)C50 values are above 1 mg/L for fish, invertebrates and algae. C12-isoAS Na (CAS 94200-74-5) does not need to be classified and labelled as environmental hazard according to Directive 67/548/EEC.