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EC number: 204-679-6 | CAS number: 124-09-4
- 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
In an activated sludge respiration inhibition test according to OECD 209 (2010) nitrification proved to be the most sensitive endpoint (highest test item concentration: 1000 mg/L):
EC50 (3h; total respiration): 1558 mg/L;
EC50 (3h; heteretrophic respiration): >> 1000 mg/L;
EC50 (3h; nitrification): 291 mg/L;
Key value for chemical safety assessment
- EC50 for microorganisms:
- 291 mg/L
Additional information
In the reliable key study (RL1; GLP) the effect of the test item Hexamethylenediamine on the respiration of heterotrophic and nitrifying bacteria in activated sludge after 3 hours exposure was investigated in a static test system according to OECD 209 (2010). Five test item concentrations were applied (1000, 313, 97.7, 30.5, and 9.54 mg/L).
A concentration-response relationship was observed for inhibition of total and heterotrophic respiration. With heterotrophic respiration, however, inhibition was less than 50% of the control, so an EC50 was not calculated.
Also, for nitrification, inhibition followed a concentration-response relationship. At the lowest concentration level tested, however, there was considerable stimulation of nitrification (50.6% stimulation relative to the control), rather than inhibition. Non-GLP pre-tests performed with sludge from the same source, showed similar results (25% and 47% stimulation at 1.6 and 8 mg/L). The results of a further range-finding test performed with a sludge from a different source were equivocal in the low dose range (34%, -8% and -25% inhibition at 1.6, 8 and 40 mg/L; negative inhibition = stimulation). In conclusion, these data may indicate a stimulating effect of the test item in the low dose range, in any case considerable variability is observed at the lowest concentration levels. Therefore, the EC10 for nitrification is associated with considerable uncertainty and is therefore not reported here. All validity criteria specified by the guideline were fulfilled.
Nitrification proved to be the most sensitive endpoint:
EC50 (3h; total respiration): 1558 mg/L;
EC50 (3h; heteretrophic respiration): >> 1000 mg/L;
EC50 (3h; nitrification): 291 mg/L.
In a supporting study (scientific publication, RL3), an indicative IC50 for hexamethylenediamine of 85 mg/L was reported. In this work, several compounds were tested for nitrification inhibition using a stock culture of autotrophic nitrifiying bacteria as inoculum. By the authors, this degree of inhibitory action was considered to be "not likely to cause problems in waste water treatment plants" compared with other, more potent inhibitors. While these data seem scientifically valid, pure cultures (i.e. culture of autotrophic nitrifying bacteria instead of activated sludge) were used and actual relevance for STPs is questionable. Further, no raw data are presented and the rate constants were determined from only 3 time points.
A further study report is available. Colonies of Pseudomonas putida were exposed to increasing concentrations of test substance for 20 hours with and without pH neutralization. The bacterial density was measured by optical density at different time intervals in four replicates and EC10 was then determined. At the end of the test, EC10 of pH-neutralized test solutions was calculated as 12500 mg/L.
Concluding, for risk assessment purposes (derivation of the PNEC_STP-microorganisms) nitrification inhibition is the most relevant and sensitive endpoint and the EC50 (3h, nitrification) of 291 mg/L as determined in the reliable key study will be used.
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