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EC number: 202-715-5 | CAS number: 98-94-2
- 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
DMCHA is considered as acutely harmful to aquatic organisms, however observed effects on mortality at higher test concentrations may be related to elevated pH values.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 28 mg/L
Additional information
The short-term toxicity to fish was examined in a GLP-study based on OECD guideline 203 with Oncorhynchus mykiss as test organism (Mayes et al, 1989). Chemical analysis of test item concentrations resulted in recovery rate of 64 - 137.5% of nominal concentrations with standard deviations of 11 - 60 %. The 96 hour LC50 value was calculated to be 28.1 mg/L (95% CI: 22.0 to 34.9 mg/L). Observations after 3 h of exposure showed, that there was 100% mortality at 43.9 mg/L and above; the pH at these concentrations exceeded 9.0 and may have contributed to mortality. Optimal pH range according to OECD guideline 203 is 6 - 8.5.
Results of a non-GLP study, conducted with Leuciscus idus and according to the German Standard Test Guideline, DIN 38 412 L15, 1982 (which is comparable to OECD 203) support these findings (BASF AG, 1988). No analytical verification was performed, therefore results of the study were based on nominal exposure concentrations. However it is assumed that the test concentrations remained stable over the exposure period based on results of the study by Mayes et al. (1989) and a sufficient water solubility, a low vapour pressure (3.17 hPa at 25 °C, BASF AG, 1970, BASFAG170.394.1) a low Henry's Law constant (3.01 Pa*m³/mol, VP/WS method, BASF SE, 2015) and a low adsorption potential (log Kow = 2.01, BASF AG, 1988, Rep. no. 122968/01). The 96h LC50 was observed to be > 21.5 mg/L and <46.5 mg/L, the corresponding NOEC was 21.5 mg/L. After pH adjustment of the highest test concentration (100 mg/L) the 96h LC50 was >100 mg/L and the corresponding NOEC was 100 mg/L.
Based on these results, DMCHA is considered to be harmful to aquatic organisms. However, observed effects on mortality at higher test item concentrations may be related to high pH values, which exceeded 9.0. These effects on mortality were not observed, after pH-adjustment.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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