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EC number: 203-818-8 | CAS number: 110-95-2
- 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
Toxicity to other above-ground organisms
Administrative data
- Endpoint:
- toxicity to other above-ground organisms
- Adequacy of study:
- other information
- Reliability:
- 4 (not assignable)
Data source
Reference
- Title:
- No information
- Author:
- The Acute Oral Toxicity, Repellency, and hazard Potential of 998 chemicals to one or more Species of Wild and domestic Birds. U.S. Fish and Wildlife Service, Wildlife Research center. Archives of Environmental Contamination and Toxicology. Springer-Verlag 1983.
Materials and methods
Test guideline
- Qualifier:
- according to guideline
Test material
- Reference substance name:
- N,N,N',N'-tetramethyltrimethylenediamine
- EC Number:
- 203-818-8
- EC Name:
- N,N,N',N'-tetramethyltrimethylenediamine
- Cas Number:
- 110-95-2
- Molecular formula:
- C7H18N2
- IUPAC Name:
- N,N,N',N'-tetramethyltrimethylenediamine
- Reference substance name:
- N,N'-tetramethyltrimethylenediamine
- IUPAC Name:
- N,N'-tetramethyltrimethylenediamine
Constituent 1
Constituent 2
Test organisms
- Test organisms (species):
- other: Redwing, Starling, and Coturnix.
Results and discussion
Any other information on results incl. tables
RS-Freetext:
It was shown that redwings were significantly more sensitive than starlings, and that starlings and coturnix were not different. The difference in toxicological sensitivity between redwings and starlings was 2.1x and the difference between coturnix and redwings was 1.4x.
Tetramethylpropanediamine:
LD50 (mg/Kg) = +100
Redwing: R50 (mg/Kg) = +1
Coturnix: LD50 (mg/Kg) = +316 (m)
Applicant's summary and conclusion
- Conclusions:
- CL-Freetext:
Statistical comparisons of the correlation between redwings LD50'S and R50'S were made to determine the validity of observations made over the past 20 years indicating that avian repellent activity appears to increase with increasing acute oral toxicity.
Thus the data indicate that gross acute toxicity, as defined by the LD50, is not positively related to gross repellency as defined by the R50, at least over the small range examined.
The repellency/toxicity index or acute avian hazard index was calculated for 377 chemicals where one or both R50 and LD50 were only known. Those chemicals for which the LD50 and R50 were only known to exceed some value could not be used in subsequent calculations since no meaningful value or trend could be determined by the index.
It is the first time, to our knowledge, that an attempt has been made to equate potential hazards to an index that combines the toxicity of a compound with a behavioural measure that predicts how much of the chemical could potentially be consumed in a field situation.
Thus, field application of a highly toxic chemical that is aversive to birds could have the same or less likelihood of inducing acute avian poisoning as a less toxic chemical that was more readily accepted.
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