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Diss Factsheets
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EC number: 900-600-0 | CAS number: -
- 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)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Few data on test item; no reference substance tested; use of plastic capped vessels (substance loss?)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.1010 (Aquatic Invertebrate Acute Toxicity Test, Freshwater Daphnids)
- GLP compliance:
- not specified
- Analytical monitoring:
- no
- Details on sampling:
- No data
- Vehicle:
- not specified
- Details on test solutions:
- No data
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Strain: no data
- Source: EG&G, Bionomics laboratory
- Age at study initiation: < 24 hrs old
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 173 mg/L as CaCO3
- Test temperature:
- 21° - 23°C
- pH:
- 7.4 - 9.4
- Dissolved oxygen:
- 6.5 - 9.1 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Material, size, headspace, fill volume: plastic, 150 ml in 25
- No. of organisms per vessel: 5 (test solution preparation and addition of daphnids not clearly reported)
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): no data
- No. of vessels per vehicle control (replicates): no data (not reported, if a vehicle was used)
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: no data
- Total organic carbon: no data
- Particulate matter: no data
- Metals: no data
- Pesticides: no data
- Chlorine: no data
- Alkalinity: no data
- Ca/mg ratio: no data
- Conductivity: no data
OTHER TEST CONDITIONS
- Adjustment of pH: no data
- Photoperiod: no light/dark cycle
- Light intensity: no data
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : mortality
TEST CONCENTRATIONS
- Spacing factor for test concentrations: no data
- Range finding study
- Test concentrations: no data (5 to 8 nominal concentrations were tested, depending on the chemical) - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- LC50
- Effect conc.:
- 35 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- mortality
- Remarks on result:
- other: 25-47
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 35 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- mortality
- Remarks on result:
- other: 25-47
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 7.7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- No data
- Results with reference substance (positive control):
- No reference substance tested
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Carbon tetrachloride LC50-48h to Daphnia magna sets at 35 mg/L based on nominal concentrations
- Executive summary:
The acute toxicity of CTC to the crustacean Daphnia magna was performed based on protocols "Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians", EPA-660/3 -75 -009 (1975). Daphnids (<= 24 hrs old) were exposed to 5 to 8 nominal concentrations, and the observations were made at 24 and 48 hrs of exposure, with test completion at 48 hrs.
Hardness, dissolved oxygen concentration, temperature, and pH were measured at the initiation of the test and at the end of the exposure time.
Negative control, consisting of the same dilution water, test conditions, and test organisms, was maintained concurrently with each test.
The LC50 was calculated for 24 hrs and 48 hrs. At both observation times, the LC50 was 35 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because a long-term aquatic toxicity study on invertebrates is available
Referenceopen allclose all
Description of key information
The study does not need to be conducted because long-term aquatic studies exist for each constituents.
However, to validate and support long term fish value of carbone tetrachloride (Roderer,1990), all aquatic hazard values of CTC have been compared (see section 6.1.2):
Toxicity of CTC to Daphnia magna following OECD 202 (LeBlanc, 1980):
LC50 (48h)=35 mg/L
Key value for chemical safety assessment
Additional information
The study does not need to be conducted because long-term aquatic studies exist for each constituent.
Nevertheless, the short term toxicity to invertebrates has been studied on the main constituent of Flux1: carbon tetrachloride or CTC.
The acute toxicity of CTC to the crustacean Daphnia magna was performed based on protocols "Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians", EPA-660/3 -75 -009 (1975) by Leblanc (1980). Daphnids (<= 24 hrs old) were exposed to 5 to 8 nominal concentrations, and the observations were made at 24 and 48 hrs of exposure, with test completion at 48 hrs. Hardness, dissolved oxygen concentration, temperature, and pH were measured at the initiation of the test and at the end of the exposure time.
Negative control, consisting of the same dilution water, test conditions, and test organisms, was maintained concurrently with each test.
The LC50 was calculated for 24 hrs and 48 hrs. At both observation times, the LC50 was 35 mg/L.
Regarding the two other constituents of Flux1, Leblanc (1980) studied also toxicity of chloroform on daphnia with an LC50(48h) of 29 mg/l. This hazard value is in the same range as the one on carbone tetrachloride (Leblanc, 1980). 1,2 -Dichloroethane is less toxic with an EC50 (48h) of 155 mg/L (Call et al. 1983).
LeBlanc GA. 1980. Acute toxicity of priority pollutants to water flea (Daphnia magna). Bulletins of Environmental Contamination and Toxicology 24, 684-691
Call, J. D., Brooke, L.T., Ahmad, N. and Richter, J.E. 1983. Toxicity and metabolism studies with EPA priority pollutants and related chemicals in freshwater organisms. EPA-600/3-83-095. Environmental Rearch Laboratory, Duluth, USA.
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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