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EC number: 228-055-8 | CAS number: 6104-30-9
- 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 terrestrial plants
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to terrestrial plants: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Field test, very long test duration covering flowering state and may therefore be used for chronic assessment. Control described, no standard test organism. Results of two tests in two years.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Field test, performed two times (two replicates), appr. 10 months duration each
- GLP compliance:
- not specified
- Analytical monitoring:
- no
- Vehicle:
- no
- Species:
- other: other terrestrial plant: Boronia megastigma Nees
- Plant group:
- Dicotyledonae (dicots)
- Test type:
- other:
- Study type:
- field study
- Substrate type:
- natural soil
- Limit test:
- no
- Remarks:
- appr. 10 months
- Key result
- Species:
- other: Boronia megastigma
- Duration:
- 10 mo
- Dose descriptor:
- NOEC
- Effect conc.:
- 323 kg/ha
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: growth and flowering
- Endpoint:
- toxicity to terrestrial plants: short-term
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Summary lacking experimental details. Cited in SIDS.
- Principles of method if other than guideline:
- other: field test
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Species:
- Lolium perenne
- Plant group:
- Monocotyledonae (monocots)
- Test type:
- other:
- Study type:
- field study
- Substrate type:
- natural soil
- Limit test:
- no
- Remarks:
- appr. 4.5 months
- Endpoint:
- toxicity to terrestrial plants: short-term
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Summary lacking experimental details. Cited in SIDS.
- Principles of method if other than guideline:
- other: field test
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Species:
- other: bermudagrass (Cynodon sp)
- Plant group:
- Monocotyledonae (monocots)
- Test type:
- other:
- Study type:
- field study
- Substrate type:
- natural soil
- Limit test:
- no
Referenceopen allclose all
With IBDU, applied up to 100 kg N per ha to Boronia (a typical Australian native plant), toxicity did not occur, because the N amount from IBDU solubilized and available to the plants at any given time was supposed to be small and thus would have been within the assimilation capacity of the plant. At all application times, IBDU gave the highest flower yield.
A 2.2 kg N/are rate (approx. 700 kg IBDU/ha) of IBDU resulted in chartreuse green ryegrass when soil pH was above 7.0. At 3.3 to 7.3 kg IBDU-N/are definite toxicity symptoms were produced at 1 month after applicaton, regardless of soil pH (chartreuse-yellow ryegrass). In all instances, toxicity symptoms had disappeared at 3 months after IBDU application. Tissue analysis showed an inverse correlation with Mn content. There was no off-color response to sulfur-coated urea or ureaform applied at equivalent N rates. The toxic symptom exhibited by the ryegrass was not typical of that due to high ammonium. It was postulated that if ammonium rather than some toxic constituent unique to IBDU is involved, the symptoms are the result of the effect of an extended period (of otherwise nonlethal level) of ammonium on soil pH and thus Fe and Mn availability.
There was no toxic response of bermudagrass to IBDU at soil pH 5.2 to 7.3 or at any combinations of IBDU with Ca(OH)2 and/or urea.
Description of key information
NOEC (10 mo): 323 kg ha-1 (Boronia megastigma)
Effects were observed at 700 kg ha-1 (Lolium perenne)
Key value for chemical safety assessment
Additional information
No guideline studies are available on the toxicity of IBDU to plants. IBDU is used as a slow releasing N-fertilizer. In two field studies the effects of IBDU application to plant growth/ flowering were studied. Both studies significantly show that IBDU is rather promotive than inhibiting to plant growth and flowering. I.e. no toxic response was noted in bermudagrass (Cynodon sp.) after application of up to 1900 kg IBDU/ha every week, whereas off-color was observed in Lolium perenne after 1 month of application of approximately 700 kg IBDU/ha (Volk and Dudeck 1976, approx. 4 months duration). With IBDU, applied up to 323 kg per ha to Boronia megastigma, toxicity did not occur (Reddy and Menary 1989, approx. 10 months duration).
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