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Diss Factsheets
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EC number: 200-756-3 | CAS number: 71-55-6
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The results of a number of studies are included in this section together with one comprehensive review. The study chosen for both freshwater and marine invertebrates were conducted in a closed system to reduce active ingredient losses by volatilisation. The best study on fresh water invertebrates for which a robust study is available is that by Abernethy et al 1986. However, the risk assessment conducted by De Rooij et al 2004 based on the EuroChlor review contains a better study Bobra et al 1984 which achieved a higher classification for reliability than the study included in the dossier. As this study has a lower LC50 value for freshwater invertebrates it is used as the endpoint. (as a matter of interest the Abernethy 1986 study restates the results from the Bobra 1983 study but calculates the LC50 incorrectly therefore the two studiesare in fact identical). For marine invertebrates the LC50 value is obtained in a similar way from the EuroChlor review.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 57.6 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 7.5 mg/L
Additional information
The results of the risk assessment De Rooij et al 2004 on theEuro Chlor review of studies available on a freshwater and marine invertebrates are shown below.
Acute studies on freshwater invertebrates
Species |
Duration |
Study type |
Endpoint |
Conc. (mg/L) |
SF 1000 (ug/L) |
Validity |
Comments |
Reference |
Daphnia magna |
48h |
S,A,C |
LC50 |
57.6 |
57.6 |
1 |
Bobra et al 1984 |
|
48h |
S,N,C |
LC50 |
59.6 |
59.6 |
2 |
immobility |
Abernethy et al 1986 |
|
48h |
S,N,C |
LC50 |
>530 |
>530 |
2 |
NOEC 530mg/L |
LeBlanc 1980 |
|
24h |
S,N |
EC50 |
2400 |
2400 |
3 |
immobility |
Bringmann & Kuhn 1982 |
Acute studies on marine invertebrates
Species |
Duration |
Study type |
Endpoint |
Conc. (mg/L) |
SF 1000 (ug/L) |
Validity |
Comments |
Reference |
Elminius modestus |
48h |
S,N,C |
LC50 |
7.5 |
7.5 |
2 |
Pearson & McConnel 1975 |
|
Artemia salina |
24h |
S,N |
EC50* 24 48 72 |
113 44 8 |
113 44 8 |
2 (3) (3) |
Lack of control data |
Sanchez-Fortun et al 1997 |
Mysidopsis bahia |
96h |
S,N |
LC50 |
31.2 |
31.2 |
4 |
US EPA 1980 |
A.salina – three stages tested (24, 48, 72h.
Key: Analysis A = Yes, N = nominal concentration. Study type S = static, SS = semi-static, FT = flow through. C = closed system.
Rating for validity 1 = valid without restriction, 2 = valid with restrictions, 3 = invalid, 4 = not assignable (inadequate data).
See also Overall Remarks in EuroChlor 1999 endpoint study report.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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