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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The existing data available had been reviewed by Euro Chlor (De Rooij et al. 2004). This review document evaluated algae studies on seven freshwater species and two marine species. A summary of the results of which are shown in the tables below. The only study rated by De Rooij et al 2004 as acceptable without restriction was the article published by Brack and Rottler (1994) on a series of chemicals. This work makes use of specific design in order to test volatile substance but it presents several drawbacks for hazard or risk assessment: apart from the fact that the species used is not among the standard ones referred to in the OECD Guideline 201, only biomass is provided. Recently, studies carried out on same substances as those tested by Brack and Rottler have delivered resullts significantly different, casting doubts on the validity of the latter.
A new study has been commissioned, under GLP conditions, according to OECD 201 and with specific technical provisions described in ISO 14442 standard dealing with algae testing of volatile substances. The results, retained as key study, gives an ErC50-72h = 41 mg/l and a NOECr = 7.8 mg/l.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 41 mg/L
- EC10 or NOEC for freshwater algae:
- 7.8 mg/L
Additional information
The study summaries evaluated by the reviewers in the Euro Chlor report are shown in table below.
Acute studies on freshwater algae.
Species |
Duration |
Study type |
Endpoint |
Conc. (mg/L) |
SF 1000 (ug/L) |
Validity |
Comments |
Reference |
Chlamydomonas reinhardtii |
72h |
S,A,C |
EC10 EC50 |
0.213 0.536 |
0.213 0.536 |
1 |
Biomass |
Brack & Rottler 1994 |
Chlorella vulgaris |
3h |
S,C |
EC50 |
153 |
153 |
2 |
14CO2 uptake |
Hutchinson et al 1980 |
Chlamydomonas angulosa |
3h |
S,C |
EC50 |
280 |
280 |
2 |
14CO2 uptake |
Hutchinson et al 1980 |
Microcytis aeruginosa |
8 days |
S |
LOEC |
350 |
350 |
3 |
Growth, pH7. |
Bringmann & Kuhn 1978 |
Scendesmus quadraticauda |
8 days |
S |
LOEC |
430 |
430 |
3 |
Growth |
Bringmann & Kuhn 1978 |
Selenastrum capricornutum, |
96h |
EC50 |
>669 |
>669 |
3 |
Oxygen production |
US EPA 1978 |
|
Chlooccales (mixed). |
24h |
EC10 |
100 |
100 |
4 |
Krebs 1985 |
Acute studies on marine algae
Species |
Duration |
Study type |
Endpoint |
Conc. (mg/L) |
SF 1000 (ug/L) |
Validity |
Comments |
Reference |
Phaeodactylum tricornutum |
? |
? |
EC50 |
5 |
5 |
2 |
14CO2 uptake |
Pearson & McConnell 1975 |
Skeletonema |
? |
? |
EC50 |
>699 |
>699 |
3 |
Growth |
US EPA 1978 |
No data is available to provide an EC10 value for marine algae is available in the literature. However as trichloroethane does not possess specific activity it is reasonable to suppose that the values would be similar to freshwater algae.
The new study commisioned in order to check validity of the results of the article published by Brack and Rottler confirms (as for other chemicals) that these results are to be considered as not valid, for some reason (experimental details lacking in the article). The new GLP compliant, carried out according to OECD 201 and specific conditions described in ISO 14442 for algae testing of volatile substances gives: ErC50-72h = 41 mg/l and a NOECr = 7.8 mg/l.
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