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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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
Based on the test results, the 96-hour LC50 for fathead minnow (Pimephales promelas) for 1,2-dichloroethane was determined to be 136 mg/L (95 % CI: 129 – 144 mg/L) based on measured concentrationsunder flow-through conditions. The no observed effect concentration (NOEC) was estimated to be 81 mg/L based on measured concentrations.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 136 mg/L
Additional information
The key study was taken as it was the best documented study, therefore it was considered as the most reliable study.
The acute toxicity of 1,2-dichloroethane to fathead minnow, Pimephales promelas, was determined in an aerated, 96-hour test. Treatments consisted of a dilution water control and the nominal concentrations of 53, 81, 185, 270 and 560 mg/L.
Based on the test results, the 96-hour LC50 for fathead minnow (Pimephales promelas) for 1,2-dichloroethane was determined to be 136 mg/L (95 % CI: 129 – 144 mg/L) based on measured concentrations. The no observed effect concentration (NOEC) was estimated to be 81 mg/L based on measured concentrations.
Further on, the following additional information on acute toxicity to fish is available (see table below).
Most of the remaining available studies are static or semi-static studies and most of them are conducted without analysis of the test concentrations. These tests are not considered for the assessment due to the high volatility of 1,2-dichloroethane. In this experiment the material showed a minimum 96 h LC50 of 66 mg/L in a static test with Micropterus salmoides with analytical monitoring (but significant, variable and to high vehicle concentrations) and a maximum 96 h LC50 of 430 mg/l in a closed static test with Lepomis macrochirus (Rinehart, W.E. 1971; Buccafusco et al. 1981).
Species |
LC50 |
Author |
Pimephales promelas |
116 mg/L |
Walbridge, C.T.et al.(1984) |
Cyprinodon variegatus |
> 130 – 230 mg/L |
Heitmuller, P.T.et al.(1981) |
Lepomis macrochirus |
550 mg/L |
Dawson, G.W.et al.(1975-1976) |
Oncorhynchus mykiss |
326 mg/L (95 % CI: 324-350 mg/L) |
Bartlett, E.A. (1979) |
Leuciscus idus melanotus |
406 mg/L (48 h) |
Juhnke, I. & Luedemann, D. (1978) |
Limanda limanda |
115 mg/L |
Pearson, C.R. & McConnell (1975) |
Pimephales promelas |
118 mg/L |
Veith, G.D.et al.(1983) |
Lepomis macrochirus |
430 mg/L (95 % CI: 230 – 710 mg/L) |
Buccafusco, R.J.et al.(1981) |
Lepomis macrochirus |
94 mg/L (95 % CI: 79.7 – 110.9 mg/L) |
Rinehart, W.E. (1971) |
Micropterus salmoides |
66 mg/L (95 % CI: 48.9 – 89.1 mg/L) |
Rinehart, W.E. (1971) |
Cyprinidon variegatus |
> 126 – 226 mg/L |
Syracuse Res. Corp. (1978) |
Oncorhynchus mykiss |
225 mg/L |
Johnson, W.W. & Finley, M.T. (1980) Mayer, F.L. & Ellersieck, M.R. (1986) |
Leuciscus idus melanotus |
1.8 mg/L (48 h) |
Knie, J.et al.(1983) |
Poecilia reticulata |
106 mg/L (7 d) |
Koenemann, H. (1981) |
Menidia beryllina |
480 mg/L |
Dawson, G.W.et al.(1975-1976) |
Reference list
Bartlett, E.A. (1979): NTIS/OTS 0517174 # 86-870002085.
Buccafusco, R.J., Ells, S.J. & LeBlanc, G.A. (1981): Acute toxicity of priority pollutants to bluegill (Lepomis macrochirus); Bull. Environ. Contam. Toxicol. 26, 446 - 452.
Dawson, G.W.,, A.L., Drozdowski, D. & Rider, E. (1975-1976): The acute toxicity of 47 industrial chemicals to fresh and saltwater fishes; J. Hazard. Mater. 1, 303 - 318.
Heitmuller, P.T., Hollister, T.A. & Parrish, P.R. (1981): Acute toxicity of 54 industrial chemicals to sheepshead minnows (Cyprinodon variegatus); Bull. Environ. Contam. Toxicol. 27, 596 - 604.
Johnson, W.W., Finley, M.T. (1980): Handbook of Acute Toxicity of Chemicals to Fish and Aquatic Invertebrates, United States Department of the Interior Fish and Wildlife Service/ Resource Publication 137, Washington, D.C., 1-3, 83, 86.
Knie, J., Haelke, A., Juhnke, I., Schiller, W. (1983): Ergebnisse der Untersuchungen von chemischen Stoffen mit vier Biotests; Dtsch. Gewaesserkundl. Mitt. 27(3), 77-79.
Koenemann, H. (1981): Quantitative structure-activity relationships in fish toxicity studies - part 1: relationship for 50 industrial pollutants; Toxicology 19, 209-221.
Johnson, W.W., Finley, M.T. (1980): Handbook of Acute |Toxicity of Chemicals to Fish and Aquatic Invertebrates, United States Department of the Interior Fish and Wildlife Service/ Resource Publication 137, Washington, D.C., 1-3, 83, 86.
Juhnke, I., Luedemann, D. (1978): Ergebnisse der Untersuchung von 200 chemischen verbindungen auf akute Fishtoxizität mit dem Goldorfentest; Z. Wasser Abwasser Forsch. 11(5), 161-164.
Pearson, C.R., McConnell, G. (1975): Chlorinated C1 and C2 hydrocarbons in the marine environment. Proc. R. Soc. London, Ser. B. 189 (1096), 305-332.
Rinehart, W.E. (1971): NTIS/OTS 0516114 # 86-870001211.
Syracuse Res. Corp. (1978): NTIS/OTS 0511060 # 40-7848049.
Veith, G.D., Call, D.J. & Roff, J.C. et al. (1983): Structure–Toxicity Relationships for the Fathead Minnow,Pimephales promelas: Narcotic Industrial Chemicals; Can. J. Fish. Aquat. Sci. 40, 743-748.
Walbridge, C.T., Fiandt, J.T., Phipps, G. L. & Holcombe, G.W. (1983): Acute Toxicity of ten chlorinated aliphatic hydrocarbons to the fathead minnow (Pimephales promelas); Arch.Environ. Contam. Toxicol. 12, 661 - 666.
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