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EC number: 247-557-8 | CAS number: 26264-06-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 0.28 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 0.654 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.458 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 50 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- PNEC sediment (freshwater)
- PNEC value:
- 27.5 mg/kg sediment dw
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Sediment (marine water)
- Hazard assessment conclusion:
- PNEC sediment (marine water)
- PNEC value:
- 2.75 mg/kg sediment dw
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Hazard for air
Air
- Hazard assessment conclusion:
- PNEC air
- PNEC value:
- 10 mg/m³
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- PNEC soil
- PNEC value:
- 25 mg/kg soil dw
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- PNEC oral
- PNEC value:
- 20 mg/kg food
- Assessment factor:
- 10
Additional information
Table Summary of Aquatic Toxicity of Calcium dodecylbenzenesulfonate and structural analogue or surrogate on Aquatic Organisms
AquaticToxicity |
Organism |
Species |
Test Duration |
Result(mg/L) |
Test material |
Reference |
Short-term toxicity to fish |
Fish |
Cyprinus carpio
|
48hr
|
LC50= 2.8-4.2 mg/l
|
Calcium dodecylbenzenesulphonate
|
Nishiuchi,Y., H. Iwamura, and K. Asano,1985 |
Salmo gairdneri
|
96hr
|
LC50= 3.2-5.6 mg/l
|
Sodium dodecylbenzenesulfonate
|
Douglas et al.,1986
|
||
Rita rita |
96hr |
LC50=6.926- 7.16 mg/l |
Sodium dodecylbenzenesulfonate |
Roy, 1988 |
||
Leuciscus idus |
96hr |
LC50=4.1mg/l |
Dodecylbenzenesulfonic acid |
Knie, V.J.et al.,1983 |
||
Brachydanio rerio |
96hr |
LC50=10 mg/l |
Dodecylbenzenesulfonic acid |
Hoechst AG 1988 |
||
Fishes species (freshwater fish) |
96hr |
LC50=1.74 mg/l (calculated) |
Calcium dodecylbenzenesulphonate
|
USEPA, 2011
|
||
Oryzias latipes |
48hr
|
LC50= 3-5.3 mg/l
|
Calcium dodecylbenzenesulphonate
|
Nishiuchi,Y., H. Iwamura, and K. Asano,1985 |
||
|
|
Misgurnus anguillicaudatus |
48hr
|
LC50= 3.3-6 mg/l
|
Calcium dodecylbenzenesulphonate
|
Nishiuchi,Y., H. Iwamura, and K. Asano,1985 |
|
|
Fishes species (freshwater fish) |
24 hr |
LC50=4.5-6.4 mg/l |
Sodium dodecylbenzenesulfonate |
Lundahl,P., and R. Cabridenc, 1978 |
Long-term toxicity to fish |
Fish |
Fishes species (freshwater fish) |
30 day |
NOEC =0.23 mg/l (calculated) |
Calcium dodecylbenzenesulphonate
|
USEPA, 2011
|
Tilapia mossambica |
90 day
|
NOEC =0.25mg/l |
Benzenesulfonic acid, C10-13-alkyl derivs., sodium salts |
Chattopahyay, D.N. and Konar, S.K.,1985 |
||
Lepomis macrochirus |
28 day
|
NOEC =1mg/l |
C11.6 LAS |
Maki AW, 1981 |
||
Pimephales promelas |
32 day
|
EC20=1 mg/l |
Dodecylbenzenesulfonic acid
|
Versteeg DJ and Rawlings JM, 2003 |
||
Pimephales promelas |
28 day
|
NOEC =0.9 mg/l |
C11.8 LAS |
Maki AW, 1979 |
||
Short-term toxicity to aquatic invertebrates |
Invertebrates |
Daphnia magna |
48hr |
LC50= 3.5mg/l |
C12 LAS |
Kimerle and Swisher, 1977 |
Daphnid species |
48hr |
LC50=1.276 mg/l (calculated) |
Calcium dodecylbenzenesulphonate
|
USEPA, 2011
|
||
Daphnia pulex Daphnia carinata
|
48hr |
LC50=40 mg/l |
Calcium dodecylbenzenesulphonate
|
Nishiuchi,Y., H. Iwamura, and K. Asano,1985
|
||
Daphnia magna |
24hr |
EC50=12 mg/l |
Dodecylbenzenesulfonic acid
|
Knie, V.J.,et al.,1983 |
||
Daphnia magna |
48hr |
EC50=5.88 mg/l |
Dodecylbenzenesulfonic acid
|
Galassi et al. 1993 |
||
Daphnia magna |
48hr |
EC50=6.3-9.5 mg/l |
Sodium dodecylbenzenesulfonate
|
Oda,S., N. Tatarazako, H. Watanabe, M. Morita, and T. Iguchi, 2006 |
||
Daphnia magna |
24hr |
EC50=12-17 mg/l |
Sodium dodecylbenzenesulfonate
|
Lundahl,P., and R. Cabridenc,1978 |
||
Tisbe bulbisetosa (saltwater Invertebrates) |
48hr |
LC50=4.58 -5.12 mg/l |
Dodecylbenzenesulfonate (DBS) |
Venezia LD, et al.1980 |
||
Long-term toxicity to aquatic invertebrates |
Invertebrates |
Daphnid species |
30 day |
NOEC =0.253mg/l (calculated) |
Calcium dodecylbenzenesulphonate
|
USEPA, 2011
|
Daphnia magna |
21 day |
NOEC =1.25-3.25mg/l |
Benzenesulfonic acid, C10-13-alkyl derivs., sodium salts |
Taylor, M.J.,1985 |
||
Daphnia magna |
21 day |
NOEC =1.65mg/l |
Sodium dodecylbenzenesulfonate |
Radix P,et al.2000 |
||
Ceriodaphnia dubia |
7 day |
NOEC =4mg/l |
Sodium dodecylbenzene sulfinate |
Moore,S.B., R.A. Diehl, J.M. Barnhardt, and G.B. Avery,1987 |
||
Daphnia magna |
21 day |
NOEC =1.18mg/l |
C11.8 LAS |
Maki, A.W. 1979 |
||
Toxicity to aquatic algae and cyano-bacteria |
Algae |
Pseudokirchneriella subcapitata |
72hr |
NOEC = 7.9mg/l EC50= 65.4 mg/l (growth rate) EC50=21 (biomass) |
Dodecylbenzenesulfonic acid |
MOE, 2008 |
Green Algae |
30 day |
NOEC =1.266mg/l (calculated) EC50=2.736mg/l (calculated) |
Calcium dodecylbenzenesulphonate
|
USEPA, 2011
|
||
Selenastrum capricornutum (Algae) |
96hr
|
EC50=29mg/l |
Dodecylbenzenesulfonic acid |
Galassi et al.1992 |
||
Toxicity to aquatic plants other than algae |
aquatic plants |
Lemna minor |
7 day |
EC50=2.7mg/l NOEC =0.9mg/l |
C11.8 LAS |
Bishop, W.E. et al1981. |
Toxicity to microorganisms |
Microorganisms |
Activated sludge |
3hr |
EC50= 500-723mg/l |
Na-12C LAS |
Verge and, 1996 |
Toxicity to other aquatic organisms |
Marine mussel |
Mytilus galloprovincialis (saltwater) |
7 day |
NOEC =32.19mg/kg/dw |
C12-LAS |
Marin, M.G., Pivotti, L., Campesan, G., Turchetto, M. and Tallandini, L.,1994 |
Conclusion on classification
The Calcium dodecylbenzenesulfonate does not meet the criteria to be classified for environmental hazards. Based on the hazard assessment of Calcium dodecylbenzenesulfonate in section 2.1 and 2.2.in IUCLID 6., available data for the substance and following the “Guidance on Information Requirement and Chemical Safety Assessment R.10, it is concluded that does not meet the criteria to be classified for environmental hazardsaccording to the criteria described in Directive 67/548 and in the CLP Regulation:
Directive 67/548 |
N; R50 R52 R53 N;R50/53 N;R51/53 R52/53 N;R59 |
CLP Regulation |
H400 Aquatic. Acute 1 Very toxic to aquatic life H413 Aquatic Chronic 4 May cause long lasting harmful effects to aquatic life H400 Aquatic acute 1, Very toxic to aquatic life H410 Aquatic chronic 1 Very toxic to aquatic life with long lasting effects H411 Aquatic Chronic 2 Toxic to aquatic life with long lasting effects H412 Aquatic Chronic 3 Harmful to aquatic life with long lasting effects EUH059 Ozone, Hazardous to the ozone layer
|
It is concluded that the substance Calcium dodecylbenzenesulphonate, meet the criteria to be classified for environmental hazards.
N;R53 - May cause long-term adverse effects in the aquatic environment
H413 Aquatic Chronic 4 May cause long lasting harmful effects to aquatic life
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