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EC number: 200-666-4 | CAS number: 67-72-1
- 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
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- Nanomaterial pour density
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- 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
- Endpoint:
- effects on growth of green algae
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 30 MARCH 2021 to 12 MAY 2021
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Version / remarks:
- No analytical monitoring
- GLP compliance:
- no
Test material
- Reference substance name:
- Tetrachloroethylene
- EC Number:
- 204-825-9
- EC Name:
- Tetrachloroethylene
- Cas Number:
- 127-18-4
- IUPAC Name:
- tetrachloroethene
- Reference substance name:
- Hexachloroethane
- EC Number:
- 200-666-4
- EC Name:
- Hexachloroethane
- Cas Number:
- 67-72-1
- Molecular formula:
- C2Cl6
- IUPAC Name:
- hexachloroethane
impurity 1
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Strain: CCAP 278/4
-Source: Culture Collection of Algae and Protozoa at Scottish Marine Institute. Successive generations grown in the Ecotoxicity laboratory of TECNALIA R&I.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 23 +/- 2°c
- pH:
- At T=0h between 7.82 and 7.96
At t=72h between 8.23 and 9.28 - Nominal and measured concentrations:
- Preliminary test concentrations: 0.5 mg/l, 5 mg/l and 50 mg/l.
Definitive test concentrations: 0.25 mg/l, 0.5 mg/l, 1 mg/l, 2 mg/l and 4 mg/l - Details on test conditions:
- Location: Algae test chamber
Test vessels: 300 ml Erlenmeyer flasks
Volume: 100 ml per flask
Initial cell concentration: 25,000 cells/mL
Type original medium of OECD TG 201 prepared according to OECD Guideline 201.
Photoperiod: continuous light
Light intensity: 4440-8880 lux (mean value of 5903 lux)
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 0.25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 0.25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.88 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- At the end of the established observation period of the definitive test (72 hours), it has been calculated that the concentration that would cause 50% growth inhibition in algae (EC50) would be 0.88 mg/l with a 95% confidence interval of 0.51 mg/l to 1.52 mg/l.
On the other hand, it has been determined that the highest concentration tested that has not produced effect on algae (NOEC) has not been tested and that the lowest that has produced effect (LOEC) has been 0.25 mg/l.
Any other information on results incl. tables
The following table shows the average cell densities of all the replicates (expressed in cells per milliliter and in neperian logarithm) of each concentration and the control at 0, 24, 48 and 72 hours. The cellular densities at 0 hours are the theoretical, due to the error of the cell counter at low densities. The densities at 24, 48 and 72 hours have been measured by cell counter.
Concentration (mg/l) | 0 h | 24 h | 48 h | 72 h | ||||
Cell density | Cell density | Cell density | Cell density | |||||
cell/ml | ln | cell/ml | ln | cell/ml | ln | cell/ml | ln | |
Control |
2.50.104 |
10.13 |
1.39.105 |
11.84 |
5.49.105 |
13.21 |
2.70.106 |
14.81 |
0.25 |
2.50.104 |
10.13 |
1.11.105 |
11.62 |
4.17.105 |
12.94 |
1.17.106 |
13.97 |
0.5 |
2.50.104 |
10.13 |
8.33.104 |
11.33 |
2.91.105 |
12.58 |
8.75.105 |
13.68 |
1 |
2.50.104 |
10.13 |
5.56.104 |
10.93 |
9.72.104 |
11.48 |
2.08.105 |
12.25 |
2 |
2.50.104 |
10.13 |
4.17.104 |
10.64 |
5.56.104 |
10.93 |
6.94.104 |
11.15 |
4 |
2.50.104 |
10.13 |
4.17.104 |
10.64 |
2.78.104 |
10.23 |
2.78.104 |
10.23 |
The results (obtained at 72 hours) of the percentages of cell growth inhibition (%Ir) with respect to the control and the respective standard deviations are presented in the following table. The percentages have been calculated based on the average specific growth rate (μ) from the mean of the three replicates. The average specific growth rate (μ) is the logarithm of the increase in cell density per unit of time.
The concentrations are presented in neperian logarithm (ln) to represent graphically the percentages of inhibition against the logarithm of the concentrations, as indicated in the OECD 201 guide.
Concentration | Ir | ||
mg/l | ln | % | Standard deviation |
0.25 | -1.39 | 17.96 | 1.56 |
0.5 | -0.69 | 24.21 | 3.07 |
1 | 0.00 | 55.00 | 4.31 |
2 | 0.69 | 79.22 | 8.53 |
4 | 1.39 | 92.71 | 6.31 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not specified
- Conclusions:
- At the end of the established observation period of the definitive test (72 hours), it has been calculated that the concentration that would cause 50% growth inhibition in algae (EC50) would be 0.88 mg/l with a 95% confidence interval of 0.51 mg/l to 1.52 mg/l.
On the other hand, it has been determined that the highest concentration tested that has not produced effect on algae (NOEC) has not been tested and that the lowest that has produced effect (LOEC) has been 0.25 mg/l.
Based on these results, it can be concluded that the tested sample is very toxic to Pseudokirchneriella subcapitata. - Executive summary:
A laboratory test according to OECD guideline 201 has been carried out to determine the growth inhibition of freshwater algae (Pseudokirchneriella subcapitata) produced by the sample «HEXACHLOROETHANE».
Exponentially growing algae were exposed to the sample for a period of 72 hours to determine its toxic effect by calculating the concentration that produces a 50% inhibition of algal growth (EC50), the highest concentration that produces no effect on the algae (NOEC) and the lowest concentration that produces an effect (LOEC).
Firstly, a preliminary test has been carried out with a wide range of concentrations and, based on the results obtained, the range of concentrations to be tested in the definitive test has been established.
The results obtained in the definitive test indicate that the concentration of the sample «HEXACHLOROETHANE» that causes a 50% inhibition of growth in algae (EC50) would be 0.88 mg/l with a 95% confidence interval of 0.51 mg/l to 1.52 mg/l. The results further indicate that the highest concentration that would produce no effect on algae (NOEC) has not been tested and that the lowest concentration tested that produced an effect on algae (LOEC) has been 0.25 mg/l. Based on these results, it can be concluded that the tested sample is very toxic to P. subcapitata.
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