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EC number: 203-458-1 | CAS number: 107-06-2
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
Single micro-organism
In a cell multiplication inhibition test the toxicity threshold for the model organism Pseudomonas putida for 1,2-dichloroethane was determined to be 135 mg/L.
Activated sludge
Based on the results of the key study the IC50 of 1,2-dichloroethane on activated sludge is 2.78 g/L.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 2 780 mg/L
- EC10 or NOEC for microorganisms:
- 135 mg/L
Additional information
Single micro-organism
In a cell multiplication inhibition test (Bringman & Kuehn, 1976) the toxicity threshold for the model organism Pseudomonas putida for 1,2-dichloroethane was determined to be 135 mg/L. This study was designed to determine the effect of 1,2-dichloroethane on micro-organisms in aequous solution by measuring the inhibition of cell growth after exposure of 16 h. The study was taken as key study, as it was the best documented study, therefore it was considered as most reliable study.
Activated sludge
The key study for a multi-species inhibition test ( Tang, Blum & Speece, 1990) was designed to determine the effects of 1,2-dichloroethane on sewage sludge micro-organisms by measuring the respiration rate after exposure to the test substance after a 3 h contact time. Two protocols were assayed: the regular OECD 209 and a serum bottle, aimed to prevent losses of volatiles. Based on the results of this study the IC50 of 1,2-dichloroethane on activated sludge is 35.5 g/L in the regular test and 2.78 g/L in the serum bottle design. The study is selected as the key study for microbial multispecies toxicity.
According to the Guidance (R.7.8.18), "In case of multiple microbial inhibition data, the PNECstp is usually derived from results obtained for the most sensitive test system available, regardless of whether this is a test with activated sludge, relevant single bacterial spicies or ciliated protozoa". Consequently, the study on Pseudomonas putida NOEC = 135 mg/L should normally be used to determine the PNECstp. However, table R.10 -6 in Guidance recommends to use Bringmann & Kuehn data only if no other test is available (it is known that volatile substances were not properly addressed by their test procedure). Finally, the IC50 = 2.78 g/L will be used for PNECstp derivation.
Following additional information on toxicity to microorganism is available:
Species |
EC50 |
Author |
Phaenobacterium phospherum |
158 mg/L (5 min) |
Qureshi, A.A. (1982) |
Phaenobacterium phospherum |
1000 mg/L (15 min) |
Hermens, J. et al. (1985) |
Pseudomonas putida |
5300 mg/L TT (30 min) |
Niemitz, W. & Trenel, J. (1979) |
Pseudomonas putida |
583 mg/L EC10 (30 min) |
Trenel, J. & Kuehn, R. (1982) |
Entosiphion sulcatum |
1127 mg/L TT |
Bringmann, G. & Kuehn, R. (1980) |
laboratory sewage sludge |
50 mg/L (4 d) |
Stuckey,et al.(1980) |
Reference list
Bringmann, G. & Kuehn, R. (1980): Water Research 14, 231 - 241.
Hermens, J. et al. (1985): Ecotoxicol. Environ. Safety 9, 17-25.
Niemitz, W. & Trenel, J. (1979): Inst.Wasser-, Boden-, Lufthyg. Bundesgesundheitsamt, Berlin, 1 - 10.
Qureshi, A.A. et al. (1982): ASTM Spec. Techn. Publ. 766,|179 - 195.
Stuckey,et al.(1980): J. Water Pollut. Control Fed. 52, 720 - 729.
Trenel, J. & Kuehn, R. (1982): Inst. Wasser-, Boden-, Lufthyg. Bundesgesundheitsamt, Juli 1982, 12 - 14, 25 - 27, Anlage 2 (23 - 28), Anlage 4 (1 - 5).
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