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EC number: 200-663-8 | CAS number: 67-66-3
- 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
A number of valid studies on the toxicity of chloroform to microorganisms are available investigating either the inhibition of respiration, ammonium consumption, gas production, or cell multiplication and using activating sludge. The most reliable study found the lowest EC50 value of 0.48 mg/L for the inhibition of ammonium consumption of Nitrosomas bacteria.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 0.48 mg/L
Additional information
In their studies, Bringmann and Kühn (1976 -1980) used the cell multiplication inhibition test to investigate the toxicity of chloroform to the bacteria Pseudomonas putida, the protozoa Entosiphon sulcatum and the flagellate Chilomonas paramaecium. The lowest EC0 value (16 hours) was found for P. putida with 125 mg/L. The EC50 values determined in the experiments of Elnabarawy et al. (1988) applying the respiration inhibition test to activated sludge exposed to chloroform for 30 minutes or three hours ranged from 840 to 1010 mg/L.
A well documented study using activated sludge has been performed by Blum and Speece (1991). Three different species were considered applying different criteria for the characterisation of adverse effects. The respiration inhibition test was applied to aerobic heterotrophs and the EC50 value (15 hours) was 640 mg/L. A second test on the inhibition of gas production was carried out with methanogens and the EC50 value determined after 48 hours was considerably lower: 0.9 mg/L. A third test with Nitrosomas bacteria, which convert ammonium nitrogen to nitrite as the first step of oxidation, investigated the inhibition of ammonium consumption and the EC50 value determined after 24 hours was lowest: 0.48 mg/L.
The available studies indicate that chloroform has the most adverse effect on ammonium converting bacteria and also on methanogenic bacteria. In contrast, aerobic bacteria seem to be more resistant with regard to exposure to chloroform. The lowest EC50 value of 0.48 mg/L is considered in the risk assessment to represent the toxicity of chloroform to microorganisms.
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